| (2) |
Emission Limitations and
Standards.
| (a) |
General
Provisions.
| 1. |
No person owning,
leasing or controlling the operation of any air contaminant sources shall
willfully, negligently or through failure to provide necessary equipment or
facilities or to take necessary precautions, cause, permit, or allow the
emission from said air contamination source or sources of such quantities of
air contaminants as will cause, or tend to cause, by themselves or in
conjunction with other air contaminants a condition of air pollution in
quantities or characteristics or of a duration which is injurious or which
unreasonably interferes with the enjoyment of life or use of property in such
area of the State as is affected thereby. Complying with any of the other
paragraphs of these rules and regulations or any subparagraphs thereof, shall
in no way exempt a person from this provision. |
| 2. |
In cases where more than one paragraph of
these regulations applies, the paragraph allowing the least emission of air
contaminants to the atmosphere shall prevail. |
| 3. |
Notwithstanding any other emission
limitation or other requirement provided in the regulations, more stringent
emission limitations or other requirements may be required of a facility as
deemed necessary by the Director to:
| (i) |
meet
any existing Federal laws or regulations; or |
| (ii) |
safeguard the public health, safety and
welfare of the people of the State of Georgia. |
|
| 4. |
Notwithstanding any other requirement of
this Chapter, in no event shall that part of a stack which came into existence
after December 31, 1970, which exceeds good engineering practice stack height
or any other dispersion technique, be taken into account for the purpose of
determining the degree of emission limitations required for control of any
pollutant for which there is an ambient air standard established under the Act
of the Federal Act. The terms and definitions of "dispersion techniques", "good
engineering practice (GEP)", "nearby" and "excessive concentration" are those
definitions found in 40 CFR
51.100(hh), (ii), (jj) and
(kk) respectively. |
| 5. |
If the Director finds, after notice and
opportunity for public hearing that a particular instance of violation or
noncompliance by a source, owner, or operator, with any emission limitation or
standard or other requirement under the Act, is de minimis (as defined pursuant
to 42 U.S.C. Section
7420 as amended) in nature, and duration, he
may, as allowed by the Act and the Federal Act, exempt such source, owner or
operator from the noncompliance penalties provided in Section 22 of the
Act. |
| 6. |
VOC Emission Standards,
Exemptions, Area Designations, Compliance Schedules and Compliance
Determinations.
| (i) |
Exemptions and Area
Designations.
| (I) |
Sources located outside
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale counties whose potential emissions of
volatile organic compounds are not more than 100 tons per year shall not be
subject to subparagraphs (u), (v), (x), (aa) through (ff) [inclusive], (hh),
(kk), (ll), (nn), and (qq) of this paragraph 391-3-1-.02(2). |
| (II) |
Sources used exclusively for chemical or
physical analysis or determination of product quality and commercial acceptance
shall not be subject to subparagraphs (t) through (ff) [inclusive], (hh)
through (nn) [inclusive], (qq), and (tt) of this paragraph 391-3-1-.02(2),
provided:
| I. |
The operation of the source is
not an integral part of the production process; and provided; |
| II. |
The emissions from the source do not
exceed 800 pounds in any calendar month; and provided; |
| III. |
The exemption from such source is
approved in writing by the Director. |
|
| (III) |
Sources located within Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Henry, Paulding, or Rockdale counties whose actual emissions of volatile
organic compounds are less than 15 pounds per day shall not be subject to
subparagraphs (u), (v), (x), (aa) through (ff) [inclusive], (kk), (ll), and
(qq) of this paragraphs 391-3-1-.02(2). |
| (IV) |
Coatings, inks and other VOC-containing
materials in use at sources of VOC emissions subject to any limitations or
requirements of subparagraphs (t) through (aa) [inclusive], (ii), (jj), (mm),
and (tt) of this paragraph 391-3-1-.02(2) shall not be subject to any
requirements of such subparagraphs, provided the source's total aggregate use
of such materials is not in excess of 55 gallons per year and such exemption is
approved in writing by the Division. |
| (V) |
Sources located within Barrow, Bartow,
Carroll, Hall, Newton, Spalding, or Walton Counties whose actual emissions of
volatile organic compounds are greater than or equal to 15 pounds per day shall
be subject to subparagraphs (u), (v), (x), (aa) through (ff) [inclusive], (hh),
(kk), (ll), (nn), and (qq) of this paragraph 391-3-1-.02(2) effective January
1, 2015. The requirements of this subparagraph (V) will no longer be applicable
if the counties specified in this subparagraph (V) are re-designated to
attainment for the 1997 National Ambient Air Quality Standard for ozone prior
to January 1, 2015. In the event the 1997 National Ambient Air Quality Standard
for ozone is violated in these counties or the counties specified in
subparagraph (III) above, the requirements of this subparagraph (V) will only
be reinstated if the Director determines that the measure is necessary to meet
the requirements of the contingency plan. |
| (VI) |
When determining applicability for a
standard specified in this subparagraph 6.(i), only those emission sources that
belong to the source category covered by each specific standard shall be
included when compared against the applicability thresholds and provisions
included in this subparagraph 6.(i). |
|
| (ii) |
Compliance Schedules.
| (I) |
All sources of VOC emissions subject to
any limitation or requirement of, or under, paragraph 391-3-1-.02(2) prior to
the effective date of this amended Rule 391-3-1-.02, shall be in compliance or
on an approved compliance schedule. |
|
| (iii) |
Compliance Determinations.
| (I) |
Compliance determinations for coatings
expressed as pounds of VOC per gallon of coating, excluding water, shall treat
organic compounds that are not defined as VOCs as water for purposes of
calculating the "excluding water" part of the coating composition. |
|
|
| 7. |
Excess Emissions.
| (i) |
Excess emissions resulting from startup,
shutdown, malfunction of any source which occur though ordinary diligence is
employed shall be allowed provided that (I) the best operational practices to
minimize emissions are adhered to, and (II) all associated air pollution
control equipment is operated in a manner consistent with good air pollution
control practice for minimizing emissions and (III) the duration of excess
emissions is minimized. |
| (ii) |
Excess
emissions which are caused entirely or in part by poor maintenance, poor
operation, or any other equipment or process failure which may reasonably be
prevented during startup, shutdown or malfunction are prohibited and are
violations of this Chapter (391-3-1). |
| (iii) |
The provisions of this paragraph 7.
shall apply only to those sources which are not subject to any requirement
under section (8) of this Rule (i.e. Rule 391-3-1-.02 ) or any requirement of
40 CFR, Part 60, as amended concerning New Source Performance
Standards. |
|
| 8. |
Emissions
Bubbles.
| (i) |
With respect to the emissions
standards and limitations contained in this Chapter 391-3-1, as such
requirements are applied to more than one process or piece of equipment at a
source or sources, the Director may allow to the extent consistent with the Act
and with the Federal Act under such conditions as he deems appropriate,
emissions bubbles provided that:
| (I) |
Such
emissions bubbles will not interfere with the attainment and maintenance of
ambient air quality standards as expeditiously as practical and does not result
in any delay in compliance by any source beyond applicable deadline dates;
and |
| (II) |
Such emissions bubbles are
equivalent in pollution reduction, enforceability, and air quality impact to
those individual process or equipment emission limits of State or federal
requirements applicable at the time of the bubble; and |
| (III) |
Such emissions bubbles are consistent
and in full compliance with the requirements of
40 CFR
52.21(PSD), 40 CFR 60 (New
Source Performance Standards) and 40 CFR 61 (NESHAPS); and |
| (IV) |
All modeling utilized in evaluating the
air quality impact of emissions bubbles shall be done in accordance with
modeling procedures acceptable to the Division. |
|
| (ii) |
Emissions bubbles involving different
pollutants, types, temporary reductions, and increases of hazardous air
pollutants are prohibited. |
| (iii) |
The affected source or facility which proposes the use of a bubble shall have
the burden of demonstrating to the satisfaction of the Director, compliance
with the requirements of this paragraph (2)(a)8. |
| (iv) |
For the purpose of this paragraph
(2)(a)8. emissions bubbles let plants decrease pollution controls at one or
more emission points in exchange for compensating increases in control at other
emission points. |
|
| 10. |
At all times,
including periods of startup, shutdown, and malfunction, any person owning,
leasing or controlling the operation of a stationary source shall maintain and
operate such source, including associated air pollution control equipment, in a
manner consistent with good air pollution control practice for minimizing
emissions. Determination of whether acceptable operating and maintenance
procedures are being used will be based on any information available to the
Division which may include, but is not limited to, monitoring results,
observations of the opacity or other characteristic of emissions, review of
operating and maintenance procedures or records, and inspection or surveillance
of the source. |
| 11. |
Startup and
Shutdown Emissions for SIP-Approved Rules
| (i) |
Upon the effective date of EPA's final approval of GA Rules Chapter 391 3 1
.02(2)(a)11. as published in the Federal Register, the provisions of
subparagraph 11.(ii) apply in lieu of GA Rule Chapter
391-3-1-.02(2)(a)7. |
| (ii) |
The
provisions of this subparagraph 11.(ii) shall apply to all sources subject to
emission limitations and standards in 391-3-1-.02(2)(b), (c), (d), (e), (f),
(g), (h), (i), (j), (k), (n), (p), (q), (r), (t), (u), (v), (w), (x), (y), (z),
(aa), (bb), (cc), (dd), (ee), (ff), (gg), (hh), (ii), (jj), (kk), (ll), (mm),
(nn), (oo), (pp), (qq), (rr), (ss), (tt), (uu), (vv), (yy), (ccc), (ddd),
(eee), (fff), (hhh), (jjj), (kkk), (lll), (mmm), (nnn), (rrr), (vvv), (yyy),
(zzz), (aaaa). The provisions of this subparagraph 11.(ii) shall also apply to
emission limitations established in accordance with the new source review
requirements in 391-3-1-.02(7)(b) and/or
391-3-1-.03(8)
unless startup and shutdown emissions have already been specifically addressed
via a federally enforceable permit.
| (I) |
Compliance Options
| I. |
Compliance with the
emission limitations and standards identified in paragraph
391-3-1-.02(2)(a)11.(ii) shall be achieved by either Option A or B below:
| A. |
Complying with the applicable emission
limitations and standards at all times, including startup and shutdown;
or |
| B. |
Complying with the applicable
emission limitations and standards for emissions resulting from normal
operations, and complying with applicable alternative work practice standards
in subparagraphs (I)III., and either (I)IV., (I)V., or (I)VI. to address
emissions resulting from startup and/or shutdown. |
|
| II. |
Excessive emissions which are caused
entirely or in part by poor maintenance, poor operation, or any other equipment
or process failure which may reasonably be prevented during startup or shutdown
are prohibited and are violations of this Chapter (391-3-1). |
| III. |
The owner or operator of a source that
chooses to comply with alternative work practice standards for startup and
shutdown shall maintain the following documentation for five years in a form
suitable for inspection and submission to the Division. Required monitoring
data (during all periods of operation) and the following documentation shall be
maintained:
| A. |
Contemporaneous operating logs
or other relevant evidence that document:
| (A) |
The date, time and duration of each period of startup or shutdown where an
alternative work practice standard was the method of compliance; |
| (B) |
Any actions taken during each period of
startup and shutdown, including which option ((ii)(I)IV., (ii)(I)V., or
(ii)(I)VI.) is followed; and |
| (C) |
Manufacturer's specifications and instructions, fire prevention protocols, and
safety protocols relied upon to demonstrate compliance with any alternative
work practice standard and records documenting implementation of
such. |
|
|
| IV. |
General Alternative Work Practice Standards Option. Process equipment and air
pollution control devices used for compliance with applicable rules in
paragraph 391-3-1-.02(2)11.(ii), shall be operated in a manner consistent with
good air pollution control practice for minimizing emissions as follows:
| A. |
General Work Practice Standard Part 1
Applicable air pollution control devices shall be started as
expeditiously as possible, providing for process and control device limitations
and providing for safety constraints for protection of personnel and equipment
and fire prevention and safety protocols such as provided by Black Liquor
Recovery Boiler Advisory Committee (BLRBAC) or National Fire Protection
Association (NFPA) codes. Documentation of such implementation of manufacturing
specifications, fire protocols, and safety protocols shall be maintained,
and;
|
| B. |
General Work
Practice Standard Part 2
During startup and shutdown periods, the owner or operator of
a source shall comply with alternative work practice standards (A) through (M)
below, as applicable, for fuel burning sources and pollution control devices
installed by the owner or operator to meet an emission limitation referenced in
paragraph 391-3-1-.02(2)(a) 11.(ii), as applicable:
| (A) |
Baghouses shall be operated, except as
provided in (H) for fuel burning equipment, and except as specified by the
manufacturer or as required by the fire prevention or safety protocols, unless
the inlet gas temperature is below the dewpoint, outside the manufacturer's
recommended operating temperature range, or if the pressure differential across
the baghouse exceeds the manufacturer's recommended maximum pressure
differential. |
| (B) |
Biofilters shall
be operated, except as specified by the manufacturer or as required by the fire
prevention or safety protocols. |
| (C) |
Carbon Adsorption Beds shall be operated, except as specified by the
manufacturer or as required by the fire prevention or safety
protocols. |
| (D) |
Condensers shall be
operated, except as specified by the manufacturer or as required by fire
prevention or safety protocols. |
| (E) |
Cyclones shall be operated, except as provided in (H) for fuel burning
equipment, and except as specified by the manufacturer or as required by fire
prevention or safety protocols. |
| (F) |
Electrostatic precipitators (ESP) shall be operated, except as provided in (H)
for fuel burning equipment, and except as specified by the manufacturer or as
required by fire prevention or safety protocols. |
| (G) |
Exhaust streams routed from one process
to another process for thermal incineration, the control process shall be
operated except as specified by the manufacturer or as required by fire
prevention or safety protocols. |
| (H) |
Fuel burning sources shall burn, during startup and shutdown periods, a "clean
fuel" as listed in item 5b. of Table 3 to 40 CFR Part 63 Subpart DDDDD, or the
cleanest fuel the unit is permitted to burn, as practicable. Particulate
matter, sulfur dioxide, and acid gas control equipment need not operate while
associated fuel burning equipment is firing natural gas, propane, distillate
oil, or combinations thereof exclusively during startup or shutdown. |
| (I) |
Selective catalytic reduction (SCR) shall
be operated, except as specified by the manufacturer or as required by the fire
prevention or safety protocols, if the catalyst inlet temperature is greater
than 600°F, or as specified by manufacturer. |
| (J) |
Selective non-catalytic reduction (SNCR)
shall be operated, except as specified by the manufacturer or as required by
the fire prevention or safety protocols, when the reaction zone temperature is
above 1600°F, or as specified by manufacturer. |
| (K) |
Scrubbers shall be operated, except as
provided in (H) for fuel burning equipment, and except as specified by the
manufacturer or as required by the fire prevention or safety
protocols. |
| (L) |
Sorbent injection
systems (e.g. carbon, zeolite, lime, trona etc.), shall be operated, except as
provided in (H) for fuel burning equipment, and except as specified by the
manufacturer or as required by the fire prevention or safety protocols, when
the exhaust gas stream temperature at the point of injection is greater than
300°F and exhaust gas velocity at the injection point exceeds 25 feet per
second based on measurement or operating parameters. |
| (M) |
Thermal oxidizer devices (including, but
not limited to, catalytic, regenerative, and recuperative systems) shall be
operated, except as required by the manufacturer or in documented fire
prevention or safety protocols. |
|
|
| V. |
Similar Process Equipment Alternative Work
Practice Standards Option. In lieu of following the General Alternative Work
Practice Standards Option in paragraph (ii)(I)IV. above, the owner or operator
of a source may follow the startup and shutdown work practice standards in
Federal rules included in 40 CFR Part 60 or 40 CFR Part 63 that address
compliance during startup and shutdown operations for subject equipment or
equipment that would be subject to the Federal rule except for rule
applicability exemptions (e.g. construction date), provided that the rule
contains specific work practice standards for startup and shutdown periods.
These rules are adopted by Georgia as 391-3-1-.02(8) and (9). For example,
coal-fired utilities may use 40 CFR 63 Subpart UUUUU (MATS rule) startup and
shutdown work practice standard to comply with Georgia Rules 391-3-1-.02(2)(b)
and (d). |
| VI. |
In lieu of following
the startup and shutdown alternative work practices in subparagraphs (ii)(I)IV.
or (ii)(I)V. above, the owner or operator of a source may comply with a source
specific alternative work practice standard for startup and shutdown periods
that has been incorporated into a federally enforceable operating permit. Any
application to incorporate such work practice standards shall include, at a
minimum, the following considerations:
| A. |
The
request is specific to the source and control device, if applicable; |
| B. |
Demonstration that compliance with the
emissions limitation during startup or shutdown is infeasible, impracticable or
unsafe; |
| C. |
The proposed alternative
work practice standard is designed to minimize emissions during startup or
shutdown periods, to the extent practicable; |
| D. |
The proposed alternative work practice
standard should require that the source is operated in a manner consistent with
good practice for minimizing emissions through planning, design, and operating
procedures; and |
| E. |
The proposed
alternative work practice standard includes provisions for monitoring and/or
recordkeeping of the operator's actions during startup and shutdown to ensure
practical enforceability of the proposed work practices. |
| F. |
Such requests shall be made through the
application for a permit, permit modification, or permit renewal pursuant to
the permit application requirements in
391-3-1-.03. The public notice
requirements specified in
391-3-1-.03(2)(i)
shall be followed for all proposed alternative work practice standards in
non-Title V permits. Public notice requirements specified in
391-3-1-.03(10)(e)8.
and 391-3-1-.03(10)(f)1.
shall be followed for all proposed alternative work practice standards in Title
V permits. |
|
|
|
| (iii) |
Paragraph 391-3-1-.02(2)(a)11.(ii)
becomes void if the June 12, 2015 publication (80 FR 33839) State
Implementation Plans: Response to Petition for Rulemaking; Restatement and
Update of EPA's SSM Policy Applicable to SIPs; Findings of Substantial
Inadequacy; and SIP Calls to Amend Provisions Applying to Excess Emissions
During Periods of Startup, Shutdown, and Malfunction is:
| (I) |
Declared or adjudged to be invalid or
unconstitutional or stayed by the United States Court of Appeals for the
Eleventh Circuit, the District of Columbia Circuit, or the United States
Supreme Court; or |
| (II) |
Withdrawn,
repealed, revoked, or otherwise rendered of no force and effect by the United
States Environmental Protection Agency, Congress, or Presidential Executive
Order. |
|
|
| 12. |
Malfunction Emissions
| (i) |
Upon the effective
date of EPA's final approval of GA Rule Chapter 391-3-1-.02(2)(a)12.(i) and
(ii) as published in the Federal Register, the provisions of this paragraph 12.
shall apply in lieu of paragraph 7. to all sources subject to emission
limitations and standards in 391-3-1-.02(2)(b), (c), (d), (e), (f), (g), (h),
(i), (j), (k), (n), (p), (q), (r), (t), (u), (v), (w), (x), (y), (z), (aa),
(bb), (cc), (dd), (ee), (ff), (gg), (hh), (ii), (jj), (kk), (ll), (mm), (nn),
(oo), (pp), (qq), (rr), (ss), (tt), (uu), (vv), (yy), (ccc), (ddd), (eee),
(fff), (hhh), (jjj), (kkk), (lll), (mmm), (nnn), (rrr), (vvv), (yyy), (zzz),
(aaaa). This paragraph 12. also applies to emission limitations established in
accordance with the new source review requirements in 391-3-1-.02(7)(b) and/or
391-3-1-.03(8)
unless malfunction emissions have already been specifically addressed via a
federally enforceable permit. |
| (ii) |
Compliance Options
| (I) |
Compliance with the
emission limitations and standards identified in paragraph
391-3-1-.02(2)(a)12.(i) shall be achieved by either:
| I. |
Complying with the applicable emission
limitations and standards at all times, including periods of malfunction
or |
| II. |
Complying with the
applicable emission limitations and standards for emissions resulting from
normal operation, and complying with a source specific malfunction work
practice standard approved into a federally enforceable air quality operating
permit to address emissions resulting from malfunction. |
|
| (II) |
Excessive emissions which are caused
entirely or in part by poor maintenance, poor operation, or any other equipment
or process failure which may reasonably be prevented during malfunction are
prohibited and are violations of this Chapter (391-3-1). |
| (III) |
The owner or operator of a source that
chooses to comply with a source specific malfunction work practice standard
approved into a federally enforceable operating permit shall maintain the
following documentation for five years in a form suitable for inspection and
submission to the Division. Required monitoring data (during all periods of
operation) and the following documentation shall be maintained:
| I. |
Contemporaneous operating logs or other
relevant evidence that document:
| A. |
The date,
time and duration of each period of malfunction where an approved source
specific malfunction work practice standard was the method of
compliance; |
| B. |
Any actions taken
during each period of malfunction; and |
| C. |
Manufacturer's specifications and
instructions, fire prevention protocols, and safety protocols relied upon to
demonstrate compliance with any source specific malfunction work practice
standard and records documenting implementation of the manufacturer
specifications and fire prevention safety protocols. |
|
|
| (IV) |
The owner or operator of a
source may comply with a source specific malfunction work practice standard for
malfunction periods that has been incorporated into a federally enforceable
operating permit. The request shall also include, as a minimum the following
considerations:
| I. |
The work practice standard
shall minimize emissions during the malfunction event and be designed to
minimize the malfunction duration. |
| II. |
Such requests shall be made through the
application for a permit, permit modification, or permit renewal pursuant to
the permit application requirements in
391-3-1-.03. The public notice
requirements specified in
391-3-1-.03(2)(i)
shall be followed for all proposed alternative work practice standards in
non-Title V permits. Public notice requirements specified in
391-3-1-.03(10)(e)8.
and 391-3-1-.03(10)(f)1.
shall be followed for all proposed alternative work practice standards in Title
V permits. |
| III. |
At all times, the
source shall be operated in a manner consistent with good practice for
minimizing emissions and the source uses best efforts regarding planning,
design, and operating procedures. The owner or operator's actions during
malfunction periods are documented by properly signed, contemporaneous
operating logs or other relevant evidence. |
| IV. |
Failure to implement or follow the source
specific malfunction work practice standard during a malfunction shall be a
violation of the Georgia Rules for Air Quality Control
391-3-1-.03(2)(g). |
| V. |
Any source that has a permit without a
malfunction work practice standard limit will be required to comply with the
applicable emission limit. |
| VI. |
Facilities that follow an approved source specific malfunction work practice
standard during a malfunction that has been addressed in the source specific
malfunction work practice standard shall be deemed in compliance.
Any application requesting a source specific malfunction work
practice standard shall also include the following considerations:
| A. |
The request is specific to the source and
control device, if applicable; |
| B. |
Demonstration that compliance with the emissions limitation during malfunction
is infeasible, impracticable or unsafe; |
| C. |
The proposed alternative work practice
standard(s) is designed to minimize emissions during malfunction periods, to
the extent practicable; |
| D. |
The
proposed alternative work practice standard should require that the source is
operated in a manner consistent with good practice for minimizing emissions
through planning, design, and operating procedures; and |
| E. |
The proposed alternative work practice
standard includes provisions for monitoring and/or recordkeeping of the
operator's actions during malfunctions to ensure practical enforceability of
the proposed work practices. |
|
|
| (V) |
Malfunctions that are not specifically
included in an approved source specific work practice, or are the result of
poor maintenance, poor operation, or otherwise reasonably preventable control
equipment or process failure, are prohibited and shall be considered violations
and reported in accordance with 391-3-1-.02(6)(b)1.(iv), if the malfunction
continues for 4 hours or more. |
| (VI) |
Unless otherwise defined in 391-3-1-.02 or in an air quality operating permit,
malfunction is defined as follows:
"Malfunction" means any unavoidable failure of air pollution
control equipment, process equipment, or process to operate in a normal and
usual manner that results in excessive emissions. Excessive emissions during
periods of routine startup and shutdown of process equipment are not considered
a malfunction. Failures caused entirely or in part by poor maintenance,
careless operations or any other upset condition, within the control of the
emission source, are not considered malfunctions.
|
|
| (iii) |
Paragraphs 391-3-1-.02(2)(a)12.(i) and
(ii) become void if the June 12, 2015 publication (80 FR 33839) State
Implementation Plans: Response to Petition for Rulemaking; Restatement and
Update of EPA's SSM Policy Applicable to SIPs; Findings of Substantial
Inadequacy; and SIP Calls to Amend Provisions Applying to Excess Emissions
During Periods of Startup, Shutdown, and Malfunction is:
| (I) |
Declared or adjudged to be invalid or
unconstitutional or stayed by the United States Court of Appeals for the
Eleventh Circuit, the District of Columbia Circuit, or the United States
Supreme Court; or |
| (II) |
Withdrawn,
repealed, revoked, or otherwise rendered of no force and effect by the United
States Environmental Protection Agency, Congress, or Presidential Executive
Order. |
|
|
| 13. |
Startup, Shutdown, and Malfunction Emissions for Certain Rules
| (i) |
Upon the effective date of EPA's final
approval of GA Rule Chapter 391-3-1-.02(2)(a)11. and/or 12. as published in the
Federal Register, the provisions of this paragraph 13. shall apply in lieu of
paragraph 7. to all sources subject to emission limitations and standards in
391-3-1-.02(2)(zz), (ggg), (iii), (ppp), (qqq), (sss), (uuu), and (www).
| (I) |
Excessive emissions resulting from
startup, shutdown, malfunction of any source which occur though ordinary
diligence is employed shall be allowed provided that (I) the best operational
practices to minimize emissions are adhered to, and (II) all associated air
pollution control equipment is operated in a manner consistent with good air
pollution control practice for minimizing emissions and (III) the duration of
excessive emissions is minimized. |
| (II) |
Excessive emissions which are caused
entirely or in part by poor maintenance, poor operation, or any other equipment
or process failure which may reasonably be prevented during startup, shutdown
or malfunction are prohibited and are violations of this Chapter
(391-3-1). |
| (III) |
The provisions of
this subparagraph 13.(i) shall not apply to emissions in excess of any
requirement under section 391-3-1-.02(8) or (9) of this Rule (i.e. any
requirement of 40 CFR Part 60, 40 CFR Part 61, or 40 CFR Part 63 ). |
|
|
|
| (b) |
Visible Emissions.
| 1. |
Except as
may be provided in other more restrictive or specific rules or subdivisions of
this Chapter, no person shall cause, let, suffer, permit, or allow emissions
from any air contaminant source the opacity of which is equal to or greater
than forty (40) percent. |
| 2. |
Upon
written application to the Director, a person owning or operating an air
pollution source may request that visible emission evaluations (opacity
measurements) be conducted during particulate emission tests for a source, for
the purpose of demonstrating compliance with a particulate emission standard.
Any such tests or evaluations shall be conducted according to methods,
procedures and requirements approved by the Division. All test results shall be
subject to verification by the Division. The correlated visible emissions
opacity determined during any such particulate emission tests which demonstrate
compliance (with results verified by the Division) may, if greater than any
applicable visible emissions opacity standard of this Chapter 391-3-1, be
established by the Director as the visible emissions standard (opacity
standard) for the source. Such visible emissions standards if so established
shall be incorporated as a condition of the operating permit for the air
pollution source. |
| 3. |
The visible
emission limitation of this subsection applies to direct sources of emissions
such as stationary structures, equipment, machinery, stacks, flues, pipes,
exhausts, vents, tubes, chimneys or similar structures. |
| 4. |
The provisions of this subsection (b),
apply only to facilities or sources subject to some other emission limitation
under this section 391-3-1-.02(2). |
|
| (c) |
Incinerators.
| 1. |
Except as specified in the section dealing
with conical burners, no person shall cause, let, suffer, permit, or allow the
emissions of fly ash and/or other particulate matter from any incinerator, in
amounts equal to or exceeding the following:
| (i) |
Units with charging rates of 500 pounds
per hour or less of combustible waste, including water, shall not emit fly ash
and/or particulate matter in quantities exceeding 1.0 pound per hour. |
| (ii) |
Units with charging rates in excess of
500 pounds per hour of combustible waste, including water, shall not emit fly
ash and/or particulate matter in excess of 0.20 pounds per 100 pounds of
charge. |
|
| 2. |
No person
shall cause, let, suffer, permit, or allow from any incinerator, visible
emissions the opacity of which is equal to or greater than twenty (20) percent
except for one 6-minute period per hour of not more than twenty-seven (27)
percent opacity. |
| 3. |
No person shall
cause or allow particles to be emitted from an incinerator which are
individually large enough to be visible to the unaided eye. |
| 4. |
No person shall operate an existing
incinerator unless:
| (i) |
it is a dual or
multiple chamber incinerator; |
| (ii) |
it is equipped with an auxiliary burner in the primary chamber for the purpose
of creating a pre-ignition temperature of 800°F; and |
| (iii) |
it has a secondary burner to control
smoke and/or odors and maintain a temperature of at least 1500°F in the
secondary chamber. |
|
| 5. |
Designs other than those mentioned in Subparagraph 4. above shall be considered
on an individual basis and will be exempt from the provisions if, in the
judgment of the Director, said design results in performance which meets the
standard set forth in paragraphs (2)(c)1., 2. and 3. above. |
| 6. |
The provisions of this Subsection (c)
shall not apply to:
| (i) |
any hazardous waste
incinerator subject to Section 391-3-11 of the Georgia Rules for Hazardous
Waste Management, 40 CFR 264, Subpart O, as adopted by reference, "Standards
for Owners and Operators of Hazardous Waste Treatment, Storage and Disposal
Facilities," as amended; |
| (ii) |
any
incinerator subject to Section 391-3-1-.02(8)(b)71. of the Georgia Rules for
Air Quality Control, "Standards of Performance for Municipal Waste Combustors
for Which Construction is Commenced After September 20, 1994," as
amended; |
| (iii) |
any incinerator
subject to the Georgia State Plan, under Section 111(d) of the federal Act, for
"Municipal Waste Combustors for Which Construction is Commenced On or Before
September 20, 1994," as amended; |
| (iv) |
any incinerator subject to Section
391-3-1-.02(8)(b)73. of the Georgia Rules for Air Quality Control "Standards of
Performance for New Stationary Sources: Hospital/Medical/Infectious Waste
Incinerators," as amended; |
| (v) |
any
incinerator subject to Section 391-3-1-.02(2)(iii) of the Georgia Rules for Air
Quality Control "Hospital/Medical/Infectious Waste Incinerators," as
amended; |
| (vi) |
any incinerator
subject to Section 391-3-1-.02(8)(b)75. of the Georgia Rules for Air Quality
Control "Standards of Performance for Commercial and Industrial Solid Waste
Incineration Units," as amended; |
| (vii) |
any incinerator subject to Section
391-3-1-.02(2)(ppp) of the Georgia Rules for Air Quality Control "Commercial
and Industrial Solid Waste Incineration Units," as amended; |
| (viii) |
any vent gas incineration devices that
are used as air pollution control equipment and boilers and industrial furnaces
that burn waste (excluding hazardous waste) as a fuel; |
| (ix) |
any incinerator subject to Section
391-3-1-.02(8)(b)20. of the Georgia Rules for Air Quality Control "Standards of
Performance for Sewage Treatment Plants," as amended; |
| (x) |
any incinerator subject to Section
391-3-1-.02(8)(b)74. of the Georgia Rules for Air Quality Control "Standards of
Performance for Small Municipal Waste Combustion Units for Which Construction
is Commenced After August 30, 1999," as amended; |
| (xi) |
any incinerator subject to Section
391-3-1-.02(8)(b)76. of the Georgia Rules for Air Quality Control "Standards of
Performance for Other Solid Waste Incinerator Units for Which Construction is
Commenced After December 9, 2004, or for Which Modification or Reconstruction
is Commenced on or After June 16, 2006," as amended; |
| (xii) |
any incinerator subject to Section
391-3-1-.02(8)(b)83. of the Georgia Rules for Air Quality Control "Standards of
Performance for New Sewage Sludge Incineration Units" as amended; or |
| (xiii) |
any incinerator subject to Section
391-3-1-.02(2)(www) of the Georgia Rules for Air Quality Control "Sewage Sludge
Incineration Units," as amended. |
|
|
| (d) |
Fuel-Burning Equipment.
| 1. |
No person shall cause, let, suffer,
permit, or allow the emission of fly ash and/or other particulate matter from
any fuel-burning equipment in operation or under construction on or before
January 1, 1972, in amounts equal to or exceeding the following:
| (i) |
for equipment less than 10 million BTU
heat input per hour:
P = 0.7 pounds per million BTU heat input;
|
| (ii) |
for equipment equal to or greater than
10 million BTU heat input per hour, and equal to or less than 2,000 million BTU
heat input per hour:
|
| (iii) |
equipment larger than 2,000 million BTU
heat input per hour:
P = 0.24 pounds per million BTU heat input.
|
|
| 2. |
No person shall cause, let,
suffer, permit, or allow the emission of fly ash and/or other particulate
matter from any fuel-burning equipment constructed after January 1, 1972, in
amounts equal to or exceeding the following:
| (i) |
for equipment less than 10 million BTU
heat input per hour:
P = 0.5 pounds per million BTU heat input;
|
| (ii) |
for equipment equal to or greater than
10 million BTU heat input per hour, and equal to or less than 250 million BTU
heat input per hour:
|
| (iii) |
for equipment greater than 250 million
BTU heat input per hour:
P = 0.10 pounds per million BTU heat input
P = allowable weight of emissions of fly ash and/or other
particulate matter in pounds per million BTU heat input
R = heat input of fuel-burning equipment in million BTU per
hour
|
|
| 3. |
No person
shall cause, let, suffer, permit, or allow the emission from any fuel-burning
equipment constructed or extensively modified after January 1, 1972, visible
emissions the opacity of which is equal to or greater than twenty (20) percent
except for one six minute period per hour of not more than twenty-seven (27)
percent opacity. |
| 4. |
No person shall
cause, let, permit, suffer, or allow the emission of nitrogen oxides
(NOX), reported as nitrogen dioxide, from any
fuel-burning equipment equal to or greater than 250 million BTU per hour of
heat input that is constructed or extensively modified after January 1, 1972,
equal to or exceeding the following:
| (i) |
when
firing coal-0.7 pounds of NOX per million BTUs of heat
input; |
| (ii) |
when firing oil-0.3
pounds of NOX per million BTUs of heat input; |
| (iii) |
when firing gas-0.2 pounds of
NOX per million BTUs of heat input; |
| (iv) |
when different fuels are burned
simultaneously in any combination the applicable standard, expressed as pounds
of NOX per million BTUs of heat input, shall be
determined by proration. Compliance shall be determined by using the following
formula:
where:
x = percent of total heat input derived from gaseous
fuel;
y = percent of total heat input derived from oil;
z = percent of total heat input derived from coal.
|
|
|
| (e) |
Particulate Emission from Manufacturing Processes.
| 1. |
Except as may be specified in other
sections of these regulations or as may be specified in a permit issued by the
Director, no person shall cause, let, permit, suffer, or allow the rate of
emission from any source, particulate matter in total quantities equal to or
exceeding the amounts specified in subparagraphs (i) or (ii), below, as
applicable. Equipment in operation, or under construction contract, on or
before July 2, 1968, shall be considered existing equipment. All other
equipment put in operation or extensively altered after said date is to be
considered new equipment.
| (i) |
The following
equations shall be used to calculate the allowable rates of emission from new
equipment:
E = 4.1 P0.67; for process input
weight rate up to and including 30 tons per hour.
E = 55 P0.11 - 40; for process
input weight rate above 30 tons per hour.
|
| (ii) |
The following equation shall be used to
calculate the allowable rates of emission from existing equipment:
E = 4.1 P0.67
E = emission rate in pounds per hour
P = process input weight rate in tons per hour.
|
|
|
| (f) |
Normal Superphosphate Manufacturing Facilities.
| 1. |
Unit emissions of fluoride for normal
superphosphate manufacturing facilities, expressed as pounds of fluoride ion
per ton of P205 or equivalent,
shall not exceed 0.40 pounds. The allowable emission of fluorides shall be
calculated by multiplying the unit emission specified above times the expressed
design capacity of the source in question. |
|
| (g) |
Sulfur Dioxide.
| 1. |
New fuel-burning sources capable of firing
fossil fuel(s) at a rate exceeding 250 million BTUs per hour heat input,
constructed or extensively modified after January 1, 1972, excluding kraft pulp
mill recovery furnaces, may not emit sulfur dioxide equal to or exceeding:
| (i) |
0.8 pounds of sulfur dioxide per million
BTUs of heat input derived from liquid fossil fuel or derived from liquid
fossil fuel and wood residue; |
| (ii) |
1.2 pounds of sulfur dioxide per million BTUs of heat input derived from solid
fossil fuel or derived from solid fossil fuel and wood residue; |
| (iii) |
When different fossil fuels are burned
simultaneously in any combination, the applicable standard expressed as pounds
of sulfur dioxide per million BTUs of heat input shall be determined by
proration using the following formula:
where:
y = percent of total heat input derived from liquid fossil
fuel;
z = percent of total heat input derived from solid fossil
fuel;
a = the allowable emission in pounds per million BTUs.
|
|
| 2. |
All fuel burning
sources below 100 million BTUs of heat input per hour shall not burn fuel
containing more than 2.5 percent sulfur, by weight. All fuel burning sources
having a heat input of 100 million BTUs per hour or greater shall not burn a
fuel containing more than 3 percent sulfur, by weight. |
| 3. |
Notwithstanding the limitations on sulfur
content of fuels stated in paragraph 2. above, the Director may allow sulfur
content greater than that allowed in paragraph 2. above, provided that the
source utilizes sulfur dioxide removal and the sulfur dioxide emission does not
exceed that allowed by paragraph 2. above, utilizing no sulfur dioxide
removal. |
|
| (h) |
Portland Cement Plants.
| 1. |
See
Section 391-3-1-.02(8) for applicable New Source Performance
Standards. |
|
| (i) |
Nitric Acid Plants.
| 1. |
No person
shall cause or allow the emission of nitrogen oxides
(NOX), expressed as nitrogen dioxide, from Nitric Acid
Plants equal to or exceeding:
| (i) |
for plants
constructed before January 1, 1972: 25 pounds of NOX
expressed as nitrogen dioxide, per ton of 100% acid produced; |
| (ii) |
for plants constructed after January 1,
1972, the applicable New Source Performance Standards of
391-3-1-.02(8). |
|
| 2. |
No
person shall operate a nitric acid plant unless the plant is equipped with a
continuous NOX monitor and recorder or an alternate
system approved by the Director. |
|
| (j) |
Sulfuric Acid Plants.
| 1. |
No person shall cause or allow the
emission of sulfur dioxide (SO2) and acid mist from
sulfuric acid plants equal to or exceeding:
| (i) |
For plants constructed before January 1,
1972, 27.0 pounds of SO2, and 0.15 pounds of acid mist
per ton of 100% acid produced; |
| (ii) |
For plants constructed or extensively modified after January 1, 1972, the
applicable New Source Performance Standards of 391-3-1.02(8). |
|
| 2. |
No person shall operate a
sulfuric acid plant unless the plant is equipped with a continuous
SO2 monitor and recorder or an approved alternate system
approved by the Director. |
|
| (k) |
Particulate Emission from Asphaltic
Concrete Hot Mix Plants.
| 1. |
No person
shall cause, let, suffer, permit, or allow the emission of particulate matter
from an Asphaltic Concrete Hot Mix Plant equal to or exceeding amounts derived
from the following formulas:
| (i) |
For existing
plants below 45 tons per hour input-E = P, pounds per hour; |
| (ii) |
For existing plants equal to or greater
than 45 tons per hour input-E = 10P0.4 pounds per
hour; |
| (iii) |
For new plants below
125 tons per hour input-E = 2.1P0.6, pounds per
hour; |
| (iv) |
For new plants equal to
or greater than 125 tons per hour input-E = 14P0.2,
pounds per hour; |
| (v) |
Equals the
allowable emission of particulate matter in pounds per hour. P equals the
process input weight rate in tons per hour; |
| (vi) |
Equipment in operation, or under
construction contract, on or before January 1, 1972, shall be considered
existing equipment. All equipment constructed or extensively altered after said
date shall be considered new. |
|
| 2. |
The New Source Performance Standards of
391-3-1-.02(8) for such asphaltic concrete plants apply to all such plants
commencing construction on or after the effective date of such
standards. |
|
| (n) |
Fugitive Dust.
| 1. |
All persons
responsible for any operation, process, handling, transportation or storage
facility which may result in fugitive dust shall take all reasonable
precautions to prevent such dust from becoming airborne. Some reasonable
precautions which could be taken to prevent dust from becoming airborne
include, but are not limited to, the following:
| (i) |
Use, where possible, of water or
chemicals for control of dust in the demolition of existing buildings or
structures, construction operations, the grading of roads or the clearing of
land; |
| (ii) |
Application of asphalt,
water, or suitable chemicals on dirt roads, materials, stockpiles, and other
surfaces which can give rise to airborne dusts; |
| (iii) |
Installation and use of hoods, fans,
and fabric filters to enclose and vent the handling of dusty materials.
Adequate containment methods can be employed during sandblasting or other
similar operations; |
| (iv) |
Covering,
at all times when in motion, open bodied trucks, transporting materials likely
to give rise to airborne dusts; |
| (v) |
The prompt removal of earth or other material from paved streets onto which
earth or other material has been deposited. |
|
| 2. |
The percent opacity from any fugitive dust
source listed in paragraph (2)(n)1. above shall not equal or exceed 20
percent. |
|
| (p) |
Particulate Emissions from Kaolin and Fuller's Earth Processes.
| 1. |
The following equations shall be used to
calculate the allowable rates of emission from kaolin and fuller's earth
process equipment constructed or extensively modified after January 1, 1972:
| (i) |
E = 3.59P0.62;
for process input weight rate up to and including 30 tons per hour; |
| (ii) |
E =
17.31P0.l6; for process input weight rate in excess
of 30 tons per hour. |
|
| 2. |
The following equation shall be used to calculate the allowable rates of
emission from kaolin and fuller's earth process equipment constructed or put in
operation on or before January 1, 1972:
| (i) |
E
= 4.1P0.67; for process input weight rate up to and
including 30 tons per hour; |
| (ii) |
E
= 55P0.11 - 40; for process input weight rate above
30 tons per hour.
E = allowable emission rate in pounds per hour;
P = process input weight rate in tons per hour.
|
|
|
| (q) |
Particulate Emissions from Cotton Gins.
| 1. |
The emission of particulate matter from
any cotton ginning operation shall not exceed the amounts specified below.
| (i) |
The following equation shall be used to
calculate the allowable rates of emission:
E = 7 B0.5
E = allowable emission rate in pounds per hour
B = number of standard bales per hour-A standard bale is
defined as a finished bale weighing 500 pounds.
|
|
| 2. |
In lieu of demonstrating compliance with
the applicable emission standard contained in 391-3-1-.02(2)(q)1.(i) the
following control devices may be utilized:
| (i) |
for emission control from low pressure exhausts, the use of screens with a mesh
size of 80 by 80 or finer, or the use of perforated condenser drums with holes
not exceeding .045 inches in diameter, or the use of a dust house. |
| (ii) |
for emission control from high pressure
exhausts, the use of high efficiency cyclones.
If compliance with the emission standard specified in
391-3-1-.02(2)(q)1.(i) is required, then the testing methodology to be utilized
shall be that specified in the Georgia Department of Natural Resources
Procedures for Testing and Monitoring Sources of Air Pollutants.
|
|
|
| (r) |
Particulate Emissions from Granular and Mixed Fertilizer Manufacturing
Units.
| 1. |
For the purpose of this
regulation the ammoniator, dryer, cooler and associated equipment will be
considered one unit. |
| 2. |
The
following equations shall be used to calculate the allowable rates of emission
from granular and mixed fertilizer manufacturing units:
| (i) |
E = 3.59P0.62;
for production weights up to and including 30 tons per hour; |
| (ii) |
E
=17.31P0.16; for production rates above 30 tons per
hour;
E = allowable emission rate in pounds per hour;
P = production rate of finished product in tons per hour.
Recycle will not be included.
|
|
|
| (s) |
Nitrogen Oxides.
(Repealed) |
| (t) |
VOC
Emissions from Automobile and Light-Duty Truck Manufacturing.
| 1. |
No person shall cause, let, permit, suffer
or allow the emissions of VOC from automobile and/or light-duty truck
manufacturing facilities to exceed:
| (i) |
1.2
pounds of VOC per gallon of coating excluding water, as a monthly weighted
average, from each electrophoretic applied prime operation; |
| (ii) |
15.1 pounds of VOC per gallon of applied
coating solids, as a daily weighted average, from each spray prime
operation; |
| (iii) |
15.1 pounds of VOC
per gallon of applied coating solids, as a daily weighted average, from each
topcoat operation; |
| (iv) |
4.8 pounds
of VOC per gallon of coating delivered to the coating applicator from each
final repair operation. If any coating delivered to the coating applicator
contains more than 4.8 pounds of VOC per gallon of coating, the limit shall be
13.8 pounds of VOC per gallon of coating solids sprayed, as a daily weighted
average. |
| (v) |
3.5 pounds of VOC per
gallon of sealer. excluding water, delivered to an applicator that applies
sealers in amounts less than 25,000 gallons during a 12 consecutive month
period; |
| (vi) |
1.0 pounds of VOC per
gallon of sealer, excluding water, delivered to a coating applicator that
applies sealers in amounts greater than 25,000 gallons during a 12 consecutive
month period; |
| (vii) |
3.5 pounds of
VOC per gallon of adhesive, excluding water, delivered to an applicator that
applies adhesives, except body glass adhesives; |
| (viii) |
6.9 pounds of VOC per gallon of
cleaner, excluding water, delivered to an applicator that applies cleaner to
the edge of body glass prior to priming; |
| (ix) |
5.5 pounds of VOC per gallon of primer,
excluding water, delivered to an applicator that applies primer to the body
glass or to the body to prepare the glass and body for bonding; |
| (x) |
1.0 pounds of VOC per gallon of adhesive,
excluding water, delivered to an applicator that applies adhesive to bond body
glass to the body; |
| (xi) |
4.4 pounds
of VOC per gallon of coating delivered to any applicator that applies clear
coating to fascias. No coating may be used that exceeds this limit; |
| (xii) |
4.4 pounds of VOC per gallon of coating
delivered to any applicator that applies base coat to fascias, on a daily
weighted average basis; |
| (xiii) |
3.5
pounds of VOC per gallon of material, excluding water, for all other materials
not subject to some other emission limitation stated in this
paragraph. |
|
| 2. |
No person
shall cause, let, permit, suffer or allow the emissions of VOC from automobile
and/or light-duty truck manufacturing facilities to exceed:
| (i) |
0.7 pounds of VOC per gallon of coating
solids applied, as a monthly weighted average, from each electrodeposition
primer (EDP) operation when the solids turnover ratio is greater than or equal
to 0.16. For purposes of this subsection an EDP operation includes application
area, spray/rinse stations, and curing oven. |
| (ii) |
Electrodeposition Primer Operation: the
value calculated by the following formula, as a monthly weighted average, from
each electrodeposition primer (EDP) operation when the solids turnover ratio is
less than 0.160 and greater than or equal to 0.040:
| (I) |
pounds of VOC per gallon of coating
solids applied
where RT = Solids Turnover
Ratio
|
|
| (iii) |
12.0
pounds of VOC per gallon of deposited solids, as a daily weighted average basis
from each of the following: primer-surfacer operation; topcoat operation;
combined primer-surfacer and topcoat operations. For purposes of this
subsection each operation includes application area, flash-off area, and
oven. |
| (iv) |
4.8 pounds of VOC per
gallon of coating, less water and less exempt solvents, as a daily weighted
average, from each final repair operation. |
| (v) |
3.5 pounds of VOC per gallon of sealer,
excluding water, delivered to an applicator that applies sealers in amounts
less than 25,000 gallons during a 12 consecutive-month period; |
| (vi) |
1.0 pounds of VOC per gallon of sealer,
excluding water, delivered to a coating applicator that applies sealers in
amounts greater than 25,000 gallons during a 12 consecutive-month
period; |
| (vii) |
250 grams of VOC per
liter of adhesive (2.08 lb/gallon), excluding water, delivered to an applicator
that applies adhesives, except body glass adhesives and weatherstrip
adhesives; |
| (viii) |
1.0 pounds of VOC
per gallon of adhesive, excluding water, delivered to an applicator that
applies adhesive to bond body glass to the body; |
| (ix) |
6.9 pounds of VOC per gallon of cleaner,
excluding water, delivered to an applicator that applies cleaner to the edge of
body glass prior to priming; |
| (x) |
5.5 pounds of VOC per gallon of primer, excluding water, delivered to an
applicator that applies glass bonding primer to the body glass or to the body
to prepare the glass and body for bonding; |
| (xi) |
4.4 pounds of VOC per gallon of coating
delivered to any applicator that applies clear coating to fascias. No coating
may be used that exceeds this limit; |
| (xii) |
4.4 pounds of VOC per gallon of coating
delivered to any applicator that applies base coat to fascias, on a daily
weighted average basis; |
| (xiii) |
200
grams of VOC per liter of coating (1.669 lb/gal), excluding water, delivered to
an applicator that applies one of the following: gasket/gasket sealing
material; bedliner; |
| (xiv) |
3.5
pounds of VOC per gallon of material, excluding water, for all other materials
not subject to some other emission limitation stated in this paragraph. This
includes but is not limited to coatings such as cavity wax, deadener, underbody
coating, interior coating, weatherstrip adhesive, and/or lubricating
wax/compound. |
|
| 3. |
The
emission limits stated in paragraphs 1. and 2. shall be achieved by the
application of low solvent technology or a system demonstrated to have
equivalent control efficiency on the basis of pounds of VOC per gallon of
solids. |
| 4. |
No person shall cause,
let, permit, suffer or allow the emissions of VOC from the use of wipe-off
solvents to exceed 1.0 pounds per unit of production as a rolling, 12-month
average. Wipe-off solvents shall include those solvents used to clean dirt,
grease, excess sealer and adhesive, or other foreign matter from the car body
in preparation for painting or other production-related operation. |
| 5. |
No person shall cause, let, permit, suffer
or allow the emission of VOCs from flush or clean paint application systems
including paint lines, tanks and applicators, unless such solvents are captured
to the maximum degree feasible by being directed into containers that prevent
evaporation into the atmosphere. |
| 6. |
No person shall store solvents or waste solvents in drums, pails, cans or other
containers unless such containers have air-tight covers which are in place at
all times when materials are not being transferred into or out of the
container. |
| 7. |
No person shall
cause, let, permit, suffer or allow the emissions of VOC from the cleaning of
oil and grease stains on the body shop floor to exceed 0.1 pounds per unit of
production. |
| 8. |
For the purpose of
this subsection; the following definitions apply:
| (i) |
"Adhesive" means any chemical substance
that is applied for the purpose of bonding two surfaces together without regard
to the substrates involved other than by mechanical means. |
| (ii) |
"Automobile" means all passenger cars or
passenger car derivatives capable of seating a maximum of 12 or fewer
passengers. |
| (iii) |
"Bedliner" means
a multi-component coating, used at an automobile or light-duty truck assembly
coating facility, applied to a cargo bed after the application of topcoat and
outside of the topcoat operation to provide additional durability and chip
resistance. |
| (iv) |
"Cavity wax" means
a coating, used at an automobile or light-duty truck assembly coating facility,
applied into the cavities of the vehicle primarily for the purpose of enhancing
corrosion protection. |
| (v) |
"Deadener" means a coating, used at an automobile or light-duty truck assembly
coating facility, applied to selected vehicle surfaces primarily for the
purpose of reducing the sound of road noise in the passenger
compartment. |
| (vi) |
"Electrodeposition primer" means a process of applying a protective,
corrosion-resistant waterborne primer on exterior and interior surfaces that
provides thorough coverage of recessed areas. It is a dip coating method that
uses an electrical field to apply or deposit the conductive coating onto the
part. The object being painted acts as an electrode that is oppositely charged
from the particles of paint in the dip tank. Also referred to as E-coat,
Uni-Prime, and ELPO Primer. |
| (vii) |
"Electrophoretic Applied Prime Operation" means the dip tank flash-off area and
bake oven(s) which are used to apply and dry or cure the initial coating on
components of automobile and light-duty truck bodies by submerging the body
components in a coating bath with an electrical potential difference between
the components and the bath, and drying or curing such coating on the
components in bake oven(s); |
| (viii) |
"Final repair" means the operations performed and coating(s) applied to
completely-assembled motor vehicles or to parts that are not yet on a
completely assembled vehicle to correct damage or imperfections in the coating.
The curing of the coatings applied in these operations is accomplished at a
lower temperature than that used for curing primer-surfacer and topcoat. This
lower temperature cure avoids the need to send parts that are not yet on a
completely assembled vehicle through the same type of curing process used for
primer-surfacer and topcoat and is necessary to protect heat sensitive
components on completely assembled vehicles. |
| (ix) |
"Gasket/gasket sealing material" means a
fluid, used at an automobile or light-duty truck assembly coating facility,
applied to coat a gasket or replace and perform the same function as a gasket.
Automobile and light-duty truck gasket/gasket sealing material includes room
temperature vulcanization (RTV) seal material. |
| (x) |
"Glass bonding primer" means a primer,
used at an automobile or light-duty truck assembly coating facility, applied to
windshield or other glass, or to body openings, to prepare the glass or body
opening for the application of glass bonding adhesives or the installation of
adhesive bonded glass. Automobile and light-duty truck glass bonding primer
includes glass bonding/cleaning primers that perform both functions (cleaning
and priming of the windshield or other glass, or body openings) prior to the
application of adhesive or the installation of adhesive bonded glass. |
| (xi) |
"In-line repair" means the operation
performed and coating(s) applied to correct damage or imperfections in the
topcoat on parts that are not yet on a completely assembled vehicle. The curing
of the coatings applied in these operations is accomplished at essentially the
same temperature as that used for curing the previously applied topcoat. Also
referred to as high bake repair or high bake reprocess. In-line repair is
considered part of the topcoat operation. |
| (xii) |
"Interior coating" means a coating,
used at an automobile or light-duty truck assembly coating facility outside of
the primer-surfacer and topcoat operations, applied to the trunk interior to
provide chip protection. |
| (xiii) |
"Light-Duty Trucks" means any motor vehicles rated 8500 pounds gross weight or
less which are designed primarily for the purpose of transportation or are
derivatives of such vehicles; |
| (xiv) |
"Lubricating wax/compound" means a protective lubricating material, used at an
automobile or light-duty truck assembly coating facility, applied to vehicle
hubs and hinges. |
| (xv) |
"Manufacturing Facility" means a facility which assembles twenty (20) or more
automobiles or light-duty trucks per day (either separately or in combination)
ready for sale to vehicle dealers. Customizers, body shops and other repainters
are not part of this definition; |
| (xvi) |
"Primer-surfacer" means an intermediate
protective coating applied over the electrodeposition primer and under the
topcoat. Primer-surfacer provides adhesion, protection, and appearance
properties to the total finish. Primer-surfacer may also be called guide coat
or surfacer. Primer-surfacer operations may include other coating(s) (e.g.,
anti-chip, lower-body anti-chip, chip-resistant edge primer, spot primer,
blackout, deadener, interior color, basecoat replacement coating, etc.) that is
(are) applied in the same spray booth(s). |
| (xvii) |
"Sealer" means a high viscosity
material, used at an automobile or light-duty truck assembly coating facility,
generally, but not always, applied in the paint shop after the body has
received an electrodeposition primer coating and before the application of
subsequent coatings (e.g., primer-surfacer). The primary purpose of automobile
and light-duty truck sealer is to fill body joints completely so that there is
no intrusion of water, gases or corrosive materials into the passenger area of
the body compartment. Such materials are also referred to as sealant, sealant
primer, or caulk. |
| (xviii) |
"Solids
turnover ratio (RT)" means the ratio of
total volume of coating solids that is added to the EDP system in a calendar
month divided by the total volume design capacity of the EDP system. |
| (xix) |
"Spray Prime Operation" means the spray
prime booth, flash-off area and bake oven(s) which are used to apply and dry or
cure a surface coating between the electrophoretic applied prime and topcoat
operations on the components of automobile and light-duty truck
bodies; |
| (xx) |
"Topcoat" means the
final coating system applied to provide the final color and/or a protective
finish. The topcoat may be a monocoat color or basecoat/clearcoat system.
In-line repair and two-tone are part of topcoat. Topcoat operations may include
other coating(s) (e.g., blackout, interior color, etc.) that is (are) applied
in the same spray booth(s). |
| (xxi) |
"Underbody coating" means a coating, used at an automobile or light-duty truck
assembly coating facility, applied to the undercarriage or firewall to prevent
corrosion and/or provide chip protection. |
| (xxii) |
"Weatherstrip adhesive" means an
adhesive, used at an automobile or light-duty truck assembly coating facility,
applied to weatherstripping materials for the purpose of bonding the
weatherstrip material to the surface of the vehicle. |
|
| 9. |
Applicability: Prior to January 1, 2015,
the requirements of this subparagraph (t) shall apply to facilities at which
actual emissions of volatile organic compounds from the use of automobile and
light-duty truck assembly coatings equal or exceed 2.7 tons per 12-month
rolling period and are located in Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale
Counties as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 1, 3, 4, 5, 6, 7,
and 8. |
|
| 10. |
Applicability.
Prior to January 1, 2015, the requirements of this subparagraph (t) shall apply
to facilities at which the potential emissions of volatile organic compounds
from the use of automobile and light-duty truck assembly coatings equal or
exceed 100 tons per year and are located outside the counties of Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Henry, Paulding, and Rockdale as follows:
| (i) |
All applicable facilities shall comply with the provisions of subparagraphs 1,
3, 4, 5, 6, 7, and 8. |
|
| 11. |
Applicability: On and after January 1,
2015, the requirements of this subparagraph (t) shall apply to facilities at
which actual emissions of volatile organic compounds from the use of automobile
and light-duty truck assembly coatings equal or exceed 2.7 tons per 12-month
rolling period and are located in Barrow, Bartow, Carroll, Cherokee, Clayton,
Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry,
Newton, Paulding, Rockdale, Spalding, and Walton Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 2, 3, 4, 5, 6, 7, and 8. |
| (ii) |
Any physical or operational changes that
are necessary to comply with the provisions specified in subparagraph 2 are
subject to the compliance schedule specified in subparagraph
14. |
|
| 12. |
On and after
January 1, 2015, the requirements of this subparagraph (t) shall apply to
facilities at which the potential emissions of volatile organic compounds from
the use of automobile and light-duty truck assembly coatings equal or exceed
100 tons per year and are located outside the counties of Barrow, Bartow,
Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale, Spalding and Walton
as follows:
| (i) |
All applicable facilities
shall comply with the provisions of subparagraphs 1, 3, 4, 5, 6, 7, and
8. |
|
| 13. |
Applicability: The
requirements of subparagraphs 11. and 12. will no longer be applicable by the
compliance deadlines if the counties specified in those subparagraphs are
re-designated to attainment for the 1997 National Ambient Air Quality Standard
for ozone prior to January 1, 2015 and such counties continue to maintain that
Standard thereafter. Instead, the provisions of subparagraphs 9. and 10. will
continue to apply on and after January 1, 2015. In the event the 1997 National
Ambient Air Quality Standard for ozone is violated in the specified counties,
the requirements of subparagraphs 11. and 12. will only be reinstated if the
Director determines that the measure is necessary to meet the requirements of
the contingency plan. |
| 14. |
Compliance Schedule:
| (i) |
An application for a
permit to construct and operate volatile organic compound emission control
systems and/or modifications of process and/or coatings used must be submitted
to the Division no later than July 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed by
November 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements specified in subparagraph 2 must be completed before January
1, 2015. |
|
|
| (u) |
VOC Emissions from Can
Coating.
| 1. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from can coating operations to
exceed:
| (i) |
2.8 pounds per gallon of coating,
excluding water, delivered to the coating applicator from sheet base coat
(exterior and interior) and overvarnish or two-piece can exterior (basecoat and
overvarnish) operations. If any coating delivered to the coating applicator
contains more than 2.8 pounds VOC per gallon, the solids equivalent limit shall
be 4.52 pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (ii) |
4.2 pounds per
gallon of coating, excluding water, delivered to the coating applicator from
two and three-piece can interior body spray and two-piece can exterior end
(spray and roll coat) operations. If any coating delivered to the coating
applicator contains more than 4.2 pounds VOC per gallon, the solids equivalent
limit shall be 9.78 pounds VOC per gallon of coating solids delivered to the
coating applicator. |
| (iii) |
5.5
pounds per gallon of coating, excluding water, delivered to the coating
applicator from three-piece side-seam spray operations. If any coating
delivered to the coating applicator contains more than 5.5 pounds VOC per
gallon, the solids equivalent limit shall be 21.8 pounds VOC per gallon of
coating solids delivered to the coating applicator. |
| (iv) |
3.7 pounds per gallon of coating,
excluding water, delivered to the coating applicator from end seal compound
operations. If any coating delivered to the coating applicator contains more
than 3.7 pounds VOC per gallon, the solids equivalent limit shall be 7.44
pounds VOC per gallon of coating solids delivered to the coating
applicator. |
|
| 2. |
The
emission limits in this subsection shall be achieved by:
| (i) |
the application of low solvent coating
technology where each and every coating meets the limit expressed in pounds VOC
per gallon of coating, excluding water, stated in paragraph 1. of this
subsection; or |
| (ii) |
the application
of low solvent coating technology where the 24-hour weighted average of all
coatings on a single coating line or operation meets the solids equivalent
limit, expressed in pounds VOC per gallon of coating solids, stated in
paragraph 1. of this subsection; averaging across lines is not allowed;
or |
| (iii) |
control equipment,
including but not limited to incineration, carbon adsorption and condensation,
with a capture system approved by the Director, provided that 90 percent of the
non-methane volatile organic compounds which enter the control equipment are
recovered or destroyed, and that overall VOC emissions do not exceed the solids
equivalent limit expressed in pounds VOC per gallon of coating solids stated in
paragraph 1. of this subsection. |
|
| 3. |
For the purpose of this subsection, the
following definitions apply:
| (i) |
"End sealing
compound" means a synthetic rubber compound which is coated onto can ends and
which functions as a gasket when the end is assembled on the can. |
| (ii) |
"Exterior base coating" means a coating
applied to the exterior of a two-piece can body to provide protection to the
metal or to provide background for the lithographic or printing
operation. |
| (iii) |
"Sheet base
coating" means a coating applied to metal in sheet form to serve as either the
exterior or interior of two-piece or three-piece can bodies or can
ends. |
| (iv) |
"Interior body spray"
means a coating sprayed on the interior of the can body to provide a protective
film between the product and the can. |
| (v) |
"Overvarnish" means a coating applied
directly over ink to reduce the coefficient of friction, to provide gloss and
to protect the finish against abrasion and corrosion. |
| (vi) |
"Three-piece can side-seam spray" means
a coating sprayed on the exterior and interior of a welded, cemented or solder
seam to protect the exposed metal. |
| (vii) |
"Two-piece can exterior end coating"
means a coating applied by roller coating or spraying to the exterior end of a
can to provide protection to the metal. |
|
|
| (v) |
VOC Emissions from Coil
Coating.
| 1. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from coil coating operations to
exceed:
| (i) |
2.6 pounds per gallon of coating,
excluding water, delivered to the coating applicator from prime and topcoat or
single coat operations. If any coating delivered to the coating applicator
contains more than 2.6 pounds VOC per gallon, the solids equivalent limit shall
be 4.02 pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (ii) |
The emission
limits in this subsection shall apply to the coating applicator(s), oven(s) and
quench area(s) of coil coating lines involved in prime and topcoat or single
coat operations. |
|
| 2. |
The
emission limits in this subsection shall be achieved by:
| (i) |
the application of low solvent coating
technology where each and every coating meets the limit of 2.6 pounds VOC per
gallon of coating, excluding water, stated in paragraph 1. of this subsection;
or |
| (ii) |
the application of low
solvent coating technology where the 24-hour weighted average of all coatings
on a single coating line or operation meets the solids equivalent limit of 4.02
pounds VOC per gallon of coating solids, stated in paragraph 1. of this
subsection; averaging across lines is not allowed; or |
| (iii) |
control equipment, including but not
limited to incineration, carbon adsorption and condensation, with a capture
system approved by the Director, provided that 90 percent of the non-methane
volatile organic compounds which enter the control equipment are recovered or
destroyed, and that overall VOC emissions do not exceed the solids equivalent
limit of 4.02 pounds VOC per gallon of coating solids stated in paragraph 1. of
this subsection. |
|
| 3. |
For
the purpose of this subsection, the following definitions apply:
| (i) |
"Coil Coating" means the coating of any
flat metal sheet or strip that comes in rolls or coils; |
| (ii) |
"Quench Area" means a chamber where the
hot metal exiting the oven is cooled by either a spray of water or a blast of
air followed by water cooling. |
|
|
| (w) |
VOC Emissions from Paper
Coating.
| 1. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from paper coating to exceed:
| (i) |
2.9 pounds per gallon of coating,
excluding water, delivered to the coating applicator from a paper coating line.
This limit shall apply to roll, knife, rotogravure and saturation coater(s) and
drying oven(s) of paper coating. If any coating delivered to the coating
applicator contains more than 2.9 pounds VOC per gallon, the solids equivalent
limit shall be 4.79 pounds VOC per gallon of coating solids delivered to the
coating applicator. |
|
| 2. |
The emission limits in subparagraph 1. shall be achieved by:
| (i) |
the application of low solvent coating
technology where each and every coating meets the limit of 2.9 pounds VOC per
gallon of coating, excluding water; or |
| (ii) |
the application of low solvent coating
technology where the 24-hour weighted average of all coatings on a single
coating line or operation meets the solids equivalent limit of 4.79 pounds VOC
per gallon of coating solids; averaging across lines is not allowed;
or |
| (iii) |
control equipment,
including but not limited to incineration, carbon adsorption and condensation,
with a capture system approved by the Director, provided that 90 percent of the
non-methane volatile organic compounds which enter the control equipment are
recovered or destroyed, and that overall VOC emissions do not exceed the solids
equivalent limit of 4.79 pounds VOC per gallon of coating solids. |
|
| 3. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from paper, film and foil coating
unless:
| (i) |
VOC emission reduction equipment
with an overall VOC control efficiency is 90 percent for each coating line is
installed and operated; or |
| (ii) |
VOC
emissions are less than 0.08 pounds per pound of coating for each coating line
except pressure sensitive tape and label coating; or |
| (iii) |
VOC emissions are less than 0.40 pounds
per pound of solids applied for each coating line except pressure sensitive
tape and label coating. |
|
| 4. |
No person shall cause, let, permit,
suffer, or allow the emissions of VOC from pressure sensitive tape and label
coating unless:
| (i) |
VOC emission reduction
equipment with an overall VOC control efficiency is 90 percent for each coating
line is installed and operated; or |
| (ii) |
VOC emissions are less than 0.067 pounds
per pound of coating for each coating line; or |
| (iii) |
VOC emissions are less than 0.20 pounds
per pound of solids applied for each coating line. |
|
| 5. |
Each owner or operator of a facility that
coats paper, film or foil including pressure sensitive tape and label coating
shall comply with the following housekeeping requirements for any affected
cleaning operation:
| (i) |
store all
VOC-containing cleaning materials and used shop towels in closed
containers; |
| (ii) |
ensure that
storage containers used for VOC-containing cleaning materials are kept closed
at all times except when depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
cleaning materials; |
| (iv) |
convey
VOC-containing cleaning materials from one location to another in closed
containers or pipes; and |
| (v) |
minimize VOC emissions from cleaning of application, storage, mixing, and
conveying equipment by ensuring that equipment cleaning is performed without
atomizing the cleaning solvent and all spent solvent is captured in closed
containers. |
|
| 6. |
For the
purpose of this subparagraph, the following definitions apply:
| (i) |
"Knife Coating" means the application of
a coating material to a substrate by means of drawing the substrate beneath a
knife that spreads the coating evenly over the full width of the
substrate; |
| (ii) |
"Paper Coating"
means the application of a coating on paper and pressure sensitive tapes,
including plastic film and metallic foil, regardless of substrate, in which the
coating is distributed uniformly across the web; |
| (iii) |
"Roll Coating" means the application of
a coating material to a substrate by means of hard rubber or steel
rolls; |
| (iv) |
"Rotogravure Coating"
means the application of a coating material to a substrate by means of a roll
coating technique in which the pattern to be applied is etched on the coating
roll. The coating material is picked up in these recessed areas and is
transferred to the substrate. |
|
| 7. |
Applicability. Prior to January 1, 2015,
the requirements of this subparagraph (w) shall apply to facilities at which
the actual emissions of volatile organic compounds from paper, film, and foil
coating, including pressure sensitive tape and label coating, equal or exceed
15 pounds per day and are located in Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale
Counties as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 1., 2., and
6. |
|
| 8. |
Applicability.
Prior to January 1, 2015, the requirements of this subparagraph (w) shall apply
to facilities at which the potential emissions of volatile organic compounds
from paper, film, and foil coating, including pressure sensitive tape and label
coating, equal or exceed 100 tons per year and are located outside the counties
of Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2., and 6. |
|
| 9. |
Applicability. On and after January 1,
2015, the requirements of this Subparagraph (w) shall apply to facilities at
which actual emissions of volatile organic compounds from paper, film, and foil
coating, including pressure sensitive tape and label coating, equal or exceed
15 pounds per day (or 2.7 tons per 12-month rolling period) for facilities
located in Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton, Paulding,
Rockdale, Spalding, and Walton Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 5. and 6. |
| (ii) |
Individual surface coating lines that
have potential emissions of volatile organic compounds from paper, film, and
foil coating, including pressure sensitive tape and label coating, that equal
or exceed 25 tons per year shall comply with the provisions of subparagraphs 3.
and 4. |
| (iii) |
Individual surface
coating lines that have potential emissions of volatile organic compounds from
paper, film, and foil coating, including pressure sensitive tape and label
coating, that do not equal or exceed 25 tons per year and are located in
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, or Rockdale County shall comply with the provisions
of subparagraphs 1. and 2. |
| (iv) |
Individual surface coating lines that have potential emissions of volatile
organic compounds from paper, film, and foil coating, including pressure
sensitive tape and label coating, that do not equal or exceed 25 tons per year
but are located at facilities that have potential emissions of volatile organic
compounds from paper coating that equal or exceed 100 tons per year and are
located in Barrow, Bartow, Carroll, Hall, Newton, Spalding, or Walton County
shall comply with the provisions of subparagraphs 1. and 2. |
| (v) |
Any physical or operational changes that
are necessary to comply with the provisions specified in subparagraphs 3., 4.,
or 5. are subject to the compliance schedule specified in subparagraph
12. |
|
| 10. |
Applicability. On
and after January 1, 2015, the requirements of this subparagraph (w) shall
apply to facilities at which potential emissions of volatile organic compounds
from paper, film, and foil coating, including pressure sensitive tape and label
coating, equal or exceed 100 tons per year and are located outside of counties
of Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale,
Spalding, and Walton Counties as follows:
| (i) |
All applicable facilities shall comply with the provisions of subparagraphs 1.,
2., and 6. |
|
| 11. |
Applicability. The requirements of subparagraphs 9. and 10. will no longer be
applicable by the compliance deadlines if the counties specified in those
subparagraphs are re-designated to attainment for the 1997 National Ambient Air
Quality Standard for ozone prior to January 1, 2015 and such counties continue
to maintain that Standard thereafter. Instead, the provisions of subparagraphs
7. and 8. will continue to apply on and after January 1, 2015. In the event the
1997 National Ambient Air Quality Standard for ozone is violated in the
specified counties, the requirements of subparagraphs 9. and 10. will only be
reinstated if the Director determines that the measure is necessary to meet the
requirements of the contingency plan. |
| 12. |
Compliance schedule.
| (i) |
An application for a permit to construct
and operate volatile organic compound emission control systems and/or
modifications of process and/or coatings used must be submitted to the Division
no later than July 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed by
November 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements of subparagraphs 3., 4., and 5. must be completed before
January 1, 2015. |
|
|
| (x) |
VOC Emissions from Fabric and Vinyl
Coating.
| 1. |
No person shall cause,
let, permit, suffer, or allow the emissions of VOC from fabric and vinyl
coating operations to exceed:
| (i) |
2.9 pounds
per gallon of coating, excluding water, delivered to the coating applicator
from a fabric coating line. If any coating delivered to the coating applicator
contains more than 2.9 pounds VOC per gallon, the solids equivalent limit shall
be 4.79 pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (ii) |
3.8 pounds per
gallon of coating, excluding water, delivered to the coating applicator from a
vinyl coating line. If any coating delivered to the coating applicator contains
more than 3.8 pounds VOC per gallon, the solids equivalent limit shall be 7.86
pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (iii) |
The emission
limits in this subsection shall apply to roll, knife, or rotogravure coater(s)
and drying oven(s) of fabric and vinyl coating lines. |
|
| 2. |
The emission limits in this subsection
shall be achieved by:
| (i) |
the application of
low solvent coating technology where each and every coating meets the limit,
expressed in pounds VOC per gallon of coating excluding water, stated in
paragraph 1. of this subsection; or |
| (ii) |
the application of low solvent coating
technology where the 24-hour weighted average of all coatings on a single
coating line or operation meets the solids equivalent limit, expressed in
pounds VOC per gallon of coating solids, stated in paragraph 1. of this
subsection; averaging across lines is not allowed: or |
| (iii) |
control equipment, including but not
limited to incineration, carbon adsorption and condensation, with a capture
system approved by the Director, provided that 90 percent of the non-methane
volatile organic compounds which enter the control equipment are recovered or
destroyed and that overall VOC emissions do not exceed the solids equivalent
limit expressed in pounds VOC per gallon of coating solids stated in paragraph
1. of this subsection. |
|
| 3. |
For the purpose of this subsection, the following definitions apply:
| (i) |
"Fabric Coating" means the coating of a
textile substrate with a knife roll, or rotogravure coater to impart properties
that are not initially present, such as strength, stability, water or acid
repellency, or appearance; |
| (ii) |
"Knife Coating" means the application of a coating material to a substrate by
means of drawing the substrate beneath a knife that spreads the coating evenly
over the full width of the substrate; |
| (iii) |
"Roll coating" means the application of
a coating material to a substrate by means of hard rubber or steel
rolls; |
| (iv) |
"Rotogravure Coating"
means the application of a coating material to a substrate by means of a roll
coating technique in which the pattern to be applied is etched on the coating
roll. The coating material is picked up in these recessed areas and is
transferred to the substrate. |
| (v) |
"Vinyl Coating" means applying a decorative or protective topcoat, or printing
on vinyl coated fabric or vinyl sheets, but shall not mean applying plastisol
coating. |
|
|
| (y) |
VOC Emissions from Metal Furniture Coating.
| 1. |
No person shall cause, let, permit,
suffer, or allow the emissions of VOC from metal furniture coating operations
to exceed:
| (i) |
3.0 pounds per gallon of
coating, excluding water, delivered to the coating applicator from prime and
topcoat or single coat operations. If any coating delivered to the coating
applicator contains more than 3.0 pounds VOC per gallon, the solids equivalent
limit shall be 5.06 pounds VOC per gallon of coating solids delivered to the
coating applicator. |
| (ii) |
The
emission limit in this subparagraph shall apply to the application area(s),
flashoff area(s) and oven(s) of metal furniture coating lines involved in prime
and topcoat or single coat operations. |
|
| 2. |
The emission limits in subparagraph 1.
shall be achieved by:
| (i) |
the application of
low solvent coating technology where each and every coating meets the limit of
3.0 pounds VOC per gallon of coating, excluding water; or |
| (ii) |
the application of low solvent coating
technology where the 24-hour or monthly weighted average of all coatings on a
single coating line or operation meets the solids equivalent limit of 5.06
pounds VOC-per-gallon of coating solids (averaging across lines is not
allowed); or |
| (iii) |
control
equipment, including but not limited to incineration, carbon adsorption and
condensation, with a capture system approved by the Director, provided that 90
percent of the nonmethane volatile organic compounds which enter the control
equipment are recovered or destroyed, and that overall VOC emissions do not
exceed the solids equivalent limit of 5.06 pounds VOC per gallon of coating
solids. |
|
| 3. |
No person
shall cause, let, permit, suffer, or allow the emissions of VOC from metal
furniture coating operations for baked coatings to exceed:
| (i) |
2.3 pounds per gallon of coating,
excluding water, delivered to the coating applicator from general
one-component, and general multi-component coatings. If any coating delivered
to the coating applicator contains more than 2.3 pounds VOC per gallon, the
solids equivalent limit shall be 3.3 pounds VOC per gallon of coating solids as
applied. |
| (ii) |
3.0 pounds per gallon
of coating, excluding water, delivered to the coating applicator from extreme
high gloss, extreme performance, heat resistant, metallic, solar absorbent and
pretreatment coatings. If any coating delivered to the coating applicator
contains more than 3.0 pounds VOC per gallon, the solids equivalent limit shall
be 5.06 pounds VOC per gallon of coating solids as applied. |
|
| 4. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from metal furniture coating
operations for air-dried coatings to exceed:
| (i) |
2.3 pounds per gallon of coating,
excluding water, delivered to the coating applicator from general one-component
coatings. If any coating contains more than 2.3 pounds VOC per gallon, the
solids equivalent limit shall be 3.3 pounds VOC per gallon of coating solids as
applied. |
| (ii) |
2.8 pounds per gallon
of coating, excluding water, delivered to the coating applicator from general
multi-component, and extreme high gloss coatings. If any coating delivered to
the coating applicator contains more than 2.8 pounds VOC per gallon, the solids
equivalent limit shall be 4.5 pounds VOC per gallon of coating solids as
applied. |
| (iii) |
3.0 pounds per
gallon of coating, excluding water, delivered to the coating applicator from
extreme performance, heat resistant, metallic, solar absorbent and pretreatment
coatings. If any coating delivered to the coating applicator contains more than
3.0 pounds VOC per gallon, the solids equivalent limit shall be 5.06 pounds VOC
per gallon of coating solids as applied. |
|
| 5. |
Each owner or operator of a facility that
coats metal furniture shall ensure that all coating application systems utilize
one or more of the application techniques stated below:
| (i) |
Electrostatic spray
application; |
| (ii) |
High volume low
pressure (HVLP) spraying; |
| (iii) |
Flow/curtain application; |
| (v) |
Dip coat application
including electrodeposition; |
| (viii) |
Air-assisted airless
spray; or |
| (ix) |
Other coating
application methods that achieve transfer efficiency equivalent to HVLP or
electrostatic spray application methods, as determined by the
Director. |
|
| 6. |
Each owner
or operator of a facility that coats metal furniture shall comply with the
following work practice standards:
| (i) |
store
all VOC-containing coatings, thinners, and coating-related waste materials in
closed containers; |
| (ii) |
ensure that
mixing and storage containers used for VOC-containing coatings, thinners, and
coating-related waste materials are kept closed at all times except when
depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
coatings, thinners, and coating-related waste materials; and |
| (iv) |
convey VOC-containing coatings,
thinners, and coating-related waste materials from one location to another in
closed containers or pipes. |
|
| 7. |
Each owner or operator of a facility that
coats metal furniture shall comply with the following housekeeping requirements
for any affected cleaning operation:
| (i) |
store all VOC-containing cleaning materials and used shop towels in closed
containers; |
| (ii) |
ensure that
storage containers used for VOC-containing cleaning materials are kept closed
at all times except when depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
cleaning materials; |
| (iv) |
convey
VOC-containing cleaning materials from one location to another in closed
containers or pipes; and |
| (v) |
minimize VOC emissions from cleaning of application, storage, mixing, and
conveying equipment by ensuring that equipment cleaning is performed without
atomizing the cleaning solvent and all spent solvent is captured in closed
containers. |
|
| 8. |
The VOC
limits specified in this subparagraphs 3. and 4. do not apply to the following
types of metal furniture coatings and/or coating operations:
| (i) |
Touch-up and repair coatings; |
| (iii) |
Safety-indicating coatings; |
| (iv) |
Solid-film lubricants; |
| (v) |
Electric-insulating and
thermal-conducting coatings; and |
| (vi) |
Coating application utilizing hand-held
aerosol cans. |
|
| 9. |
The
emission limits in subparagraphs 3. and 4. shall be achieved by:
| (i) |
the application of low solvent coating
technology where each and every coating meets the limit expressed in pounds VOC
per gallon of coating, excluding water, stated in subparagraphs 3. and 4. of
this subparagraph; or |
| (ii) |
the
application of low solvent coating technology where the 24-hour weighted
average of all coatings on a single coating line or operation meets the solids
equivalent limit expressed in pounds VOC per gallon of coating solids, stated
in subparagraphs 3. and 4. of this subparagraph; averaging across lines is not
allowed; or |
| (iii) |
control
equipment, including but not limited to incineration, carbon adsorption and
condensation, with a capture system approved by the Director, provided that 90
percent of the nonmethane volatile organic compounds which enter the control
equipment are recovered or destroyed, and that overall VOC emissions do not
exceed the solids equivalent limit, expressed in pounds VOC per gallon of
coating solids stated in subparagraphs 3. and 4. of this
subparagraph. |
|
| 10. |
For the
purpose of this subparagraph, the following definitions apply:
| (i) |
"Application Area" means the area where
the coating is applied by spraying, dipping or flow coating
techniques. |
| (ii) |
"Metal Furniture
Coating" means the surface coating of any furniture made of metal or any metal
part, which will be assembled with other metal wood, fabric, plastic or glass
parts to form a furniture piece. |
|
| 11. |
Applicability: Prior to January 1, 2015,
the requirements of this subparagraph (y) shall apply to facilities at which
the actual emissions of volatile organic compounds from the use of metal
furniture coatings equal or exceed 15 pounds per day and are located in
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2., and 10. |
|
| 12. |
Applicability. Prior to January 1, 2015,
the requirements of this subparagraph (y) shall apply to facilities at which
the potential emissions of volatile organic compounds from the use of metal
furniture coatings equal or exceed 100 tons per year and are located outside
the counties of in Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette,
Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2., and 10. |
|
| 13. |
Applicability. On and after January 1,
2015, the requirements of this subparagraph (y) shall apply to facilities at
which the actual emissions of volatile organic compounds from the use of metal
furniture coatings, before controls, equal or exceed 15 pounds per day (or 2.7
tons per 12-month rolling period) for facilities located in Barrow, Bartow,
Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale, Spalding, and Walton
Counties as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 3., 4., 5., 6.,
7., 8., 9., and 10. |
| (ii) |
Any
physical or operational changes that are necessary to comply with the
provisions specified in subparagraphs 3., 4., 5., 6., 7., 8., or 9. are subject
to the compliance schedule specified in subparagraph 16. |
|
| 14. |
On and after January 1, 2015, the
requirements of this subparagraph (y) shall apply to facilities at which the
potential emissions of volatile organic compounds from the use of metal
furniture coatings equal or exceed 100 tons per year and are located outside
the counties of Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton,
Paulding, Rockdale, Spalding, and Walton as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2., and 10. |
|
| 15. |
Applicability. The requirements of
subparagraphs 13. and 14. will no longer be applicable by the compliance
deadlines if the counties specified in those subparagraphs are re-designated to
attainment for the 1997 National Ambient Air Quality Standard for ozone prior
to January 1, 2015 and such counties continue to maintain that Standard
thereafter. Instead, the provisions of subparagraphs 11. and 12. will continue
to apply on and after January 1, 2015. In the event the 1997 National Ambient
Air Quality Standard for ozone is violated in the specified counties, the
requirements of subparagraphs 13. and 14. will only be reinstated if the
Director determines that the measure is necessary to meet the requirements of
the contingency plan. |
| 16. |
Compliance schedule:
| (i) |
An application for a
permit to construct and operate volatile organic compound emission control
systems and/or modifications of process and/or coatings used must be submitted
to the Division no later thanJuly 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed
byNovember 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements of subparagraphs 3., 4., 5., 6., 7., 8., and 9. must be completed
before January 1, 2015. |
|
|
| (z) |
VOC Emissions from Large Appliance
Surface Coating.
| 1. |
No person shall
cause, let, permit, suffer, or allow the emissions of VOC from the surface
coating of large appliances to exceed:
| (i) |
2.8
pounds per gallon of coating, excluding water, delivered to the coating
applicator from prime single or topcoat operations. If any coating delivered to
the coating applicator contains more than 2.8 pounds VOC per gallon, the solids
equivalent limit shall be 4.52 pounds VOC per gallon of coating solids
delivered to the coating applicator; |
| (ii) |
The emission limits in this subparagraph
shall apply to the application area(s), flashoff area(s) and oven(s) of large
appliance coating lines involved in prime, single or topcoat coating
operations; |
| (iii) |
The emission
limit in this subparagraph shall not apply to the use of quick drying lacquers
used for repair of scratches and nicks. |
|
| 2. |
The emission limits in subparagraph 1.
shall be achieved by:
| (i) |
the application of
low solvent coating technology where each and every coating meets the limit of
2.8 pounds VOC per gallon of coating, excluding water; or |
| (ii) |
the application of low solvent coating
technology where the 24-hour weighted average of all coatings on a single
coating line or operation meets the solids equivalent limit of 4.52 pounds VOC
per gallon of coating solids; averaging across lines is not allowed;
or |
| (iii) |
control equipment,
including but not limited to incineration, carbon adsorption and condensation,
with a capture system approved by the Director, provided that 90 percent of the
non-methane volatile organic compounds which enter the control equipment are
recovered or destroyed, and that overall VOC emissions do not exceed the solids
equivalent limit of 4.52 pounds VOC per gallon of coating solids. |
|
| 3. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from the surface coating of large
appliances using baked coatings to exceed:
| (i) |
2.3 pounds per gallon of coating, excluding water and exempt compounds,
delivered to the coating applicator general one component and general
multi-component coatings. If any coating delivered to the coating applicator
contains more than 2.3 pounds VOC per gallon, the solids equivalent limit shall
be 3.3 pounds VOC per gallon of coating solids delivered to the coating
applicator; |
| (ii) |
2.8 pounds per
gallon of coating, excluding water and exempt compounds, delivered to the
coating applicator from extreme high gloss, extreme performance, heat
resistant, metallic, and solar absorbent, and pretreatment coatings. If any
coating delivered to the coating applicator contains more than 2.8 pounds VOC
per gallon, the solids equivalent limit shall be 4.5 pounds VOC per gallon of
coating solids delivered to the coating applicator; |
|
| 4. |
No person shall cause, let, permit,
suffer, or allow the emissions of VOC from the surface coating of large
appliances using air-dried coatings to exceed:
| (i) |
2.3 pounds per gallon of coating,
excluding water and exempt compounds, delivered to the coating applicator from
general one-component coatings. If any coating delivered to the coating
applicator contains more than 2.3 pounds VOC per gallon, the solids equivalent
limit shall be 3.3 pounds VOC per gallon of coating solids delivered to the
coating applicator; |
| (ii) |
2.8 pounds
per gallon of coating, excluding water and exempt compounds, delivered to the
coating applicator from general multi-component, extreme high gloss, extreme
performance, heat resistant, metallic, solar absorbent and pretreatment
coatings. If any coating delivered to the coating applicator contains more than
2.8 pounds VOC per gallon, the solids equivalent limit shall be 4.5 pounds VOC
per gallon of coating solids delivered to the coating applicator; |
|
| 5. |
Each owner or operator of a
facility that coats large appliances shall ensure that all coating application
systems utilize one or more of the application techniques stated below:
| (i) |
Electrostatic spray
application; |
| (ii) |
High volume low
pressure (HVLP) spraying; |
| (iii) |
Flow/curtain application; |
| (v) |
Dip coat application
including electrodeposition; |
| (viii) |
Air-assisted airless
spray; or |
| (ix) |
Other coating
application methods that achieve transfer efficiency equivalent to HVLP or
electrostatic spray application methods, as determined by the
Director. |
|
| 6. |
Each owner
or operator of a facility that coats large appliances shall comply with the
following work practice standards:
| (i) |
store
all VOC-containing coatings, thinners, and coating-related waste materials in
closed containers; |
| (ii) |
ensure that
mixing and storage containers used for VOC-containing coatings, thinners, and
coating-related waste materials are kept closed at all times except when
depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
coatings, thinners, and coating-related waste materials; and |
| (iv) |
convey VOC-containing coatings,
thinners, and coating-related waste materials from one location to another in
closed containers or pipes. |
|
| 7. |
Each owner or operator of a facility that
coats large appliances shall comply with the following housekeeping
requirements for any affected cleaning operation:
| (i) |
store all VOC-containing cleaning
materials and used shop towels in closed containers; |
| (ii) |
ensure that storage containers used for
VOC-containing cleaning materials are kept closed at all times except when
depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
cleaning materials; |
| (iv) |
convey
VOC-containing cleaning materials from one location to another in closed
containers or pipes; and |
| (v) |
minimize VOC emissions from cleaning of application, storage, mixing, and
conveying equipment by ensuring that equipment cleaning is performed without
atomizing the cleaning solvent and all spent solvent is captured in closed
containers. |
|
| 8. |
The VOC
limits specified in subparagraphs 3. and 4. do not apply to the following types
of large appliance coatings and/or coating operations:
| (i) |
Touch-up and repair coatings; |
| (iii) |
Safety-indicating coatings; |
| (iv) |
Solid-film lubricants; |
| (v) |
Electric-insulating and
thermal-conducting coatings; and |
| (vi) |
Coating application utilizing hand-held
aerosol cans. |
|
| 9. |
The
emission limits in subparagraphs 3. and 4. shall be achieved by:
| (i) |
the application of low solvent coating
technology where each and every coating meets the limit expressed in pounds VOC
per gallon of coating, excluding water, stated in subparagraphs 3. and 4. of
this subparagraph; or |
| (ii) |
the
application of low solvent coating technology where the 24-hour weighted
average of all coatings on a single coating line or operation meets the solids
equivalent limit expressed in pounds VOC per gallon of coating solids, stated
in subparagraphs 3. and 4. of this subparagraph (averaging across lines is not
allowed); or |
| (iii) |
control
equipment, including but not limited to incineration, carbon adsorption and
condensation, with a capture system approved by the Director, provided that 90
percent of the nonmethane volatile organic compounds which enter the control
equipment are recovered or destroyed, and that overall VOC emissions do not
exceed the solids equivalent limit, expressed in pounds VOC per gallon of
coating solids stated in subparagraphs 3. and 4. of this
subparagraph. |
|
| 10. |
For the
purpose of this subparagraph, the following definitions apply:
| (i) |
"Application Area" means the area where
the coating is applied by spraying, dipping or flow coating
techniques. |
| (ii) |
"Single Coat"
means a single film of coating applied directly to the metal substrate omitting
the primer application. |
| (iii) |
"Large Appliances" means doors, cases, lids, panels and interior support parts
of residential and commercial washers, dryers, ranges, refrigerators, freezers,
water heaters, dishwashers, trash compactors, air conditioners and other
similar products. |
|
| 11. |
Applicability. Prior to January 1, 2015, the requirements of this subparagraph
(z) shall apply to facilities at which the actual emissions of volatile organic
compounds from the use of large appliance coatings equal or exceed 15 pounds
per day and are located in Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale Counties as
follows:
| (i) |
All applicable facilities shall
comply with the provisions of subparagraphs 1., 2., and 10. |
|
| 12. |
Applicability. Prior to
January 1, 2015, the requirements of this subparagraph (z) shall apply to
facilities at which the potential emissions of volatile organic compounds from
the use of large appliance coatings equal or exceed 100 tons per year and are
located outside the counties of Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale
Counties as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 1., 2., and
10. |
|
| 13. |
Applicability. On
and after January 1, 2015, the requirements of this subparagraph (z) apply to
facilities at which actual emissions of volatile organic compounds from the use
of large appliance coatings, before controls, equal or exceed 15 pounds per day
(or 2.7 tons per 12-month rolling period) for facilities located in Barrow,
Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette,
Forsyth, Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale, Spalding,
and Walton Counties as follows:
| (i) |
All
applicable facilities shall comply with the provisions of subparagraphs 3., 4.,
5., 6., 7., 8., 9. and 10. |
| (ii) |
Any
physical or operational changes that are necessary to comply with the
provisions specified in subparagraphs 3., 4., 5., 6., 7., 8., or 9. are subject
to the compliance schedule specified in subparagraph 16. |
|
| 14. |
Applicability. On and after January 1,
2015, the requirements of this subparagraph (z) shall apply to facilities at
which potential emissions of volatile organic compounds from the use of large
appliance coatings equal or exceed 100 tons per year and are located outside of
counties of Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton, Paulding,
Rockdale, Spalding, and Walton Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2, and 10. |
|
| 15. |
Applicability: The requirements of
subparagraphs 13. and 14. will no longer be applicable by the compliance
deadlines if the counties specified in those subparagraphs are re-designated to
attainment for the 1997 National Ambient Air Quality Standard for ozone prior
to January 1, 2015 and such counties continue to maintain that Standard
thereafter. Instead, the provisions of subparagraphs 11. and 12. will continue
to apply on and after January 1, 2015. In the event the 1997 National Ambient
Air Quality Standard for ozone is violated in the specified counties, the
requirements of subparagraphs 13. and 14. will only be reinstated if the
Director determines that the measure is necessary to meet the requirements of
the contingency plan. |
| 16. |
Compliance schedule: All existing facilities subject to this subparagraph shall
comply with the following compliance schedule:
| (i) |
An application for a permit to construct
and operate volatile organic compound emission control systems and/or
modifications of process and/or coatings used must be submitted to the Division
no later than July 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed by
November 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements of subparagraphs 3., 4., 5., 6., 7., 8., and 9. must be completed
before January 1, 2015. |
|
|
| (aa) |
VOC Emissions from Wire
Coating.
| 1. |
No person shall cause, let,
permit, suffer, or allow the emissions of VOC from wire coating operations to
exceed:
| (i) |
1.7 pounds per gallon of coating,
excluding water, delivered to the coating applicator from wire coating
operations. If any coating delivered to the coating applicator contains more
than 1.7 pounds VOC per gallon, the solids equivalent limit shall be 2.21
pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (ii) |
The emission limit
in this subsection shall apply to the oven(s) of wire coating
operations. |
|
| 2. |
The
emission limits in this subsection shall be achieved by:
| (i) |
the application of low solvent coating
technology where each and every coating meets the limit of 1.7 pounds VOC per
gallon of coating, excluding water, stated in paragraph 1. of this subsection;
or |
| (ii) |
the application of low
solvent coating technology where the 24-hour weighted average of all coatings
on a single coating line or operation meets the solids equivalent limit of 2.21
pounds VOC per gallon of coating solids, stated in paragraph 1. of this
subsection; averaging across lines is not allowed; or |
| (iii) |
control equipment, including but not
limited to incineration, carbon adsorption and condensation, with a capture
system approved by the Director, provided that 90 percent of the nonmethane
volatile organic compounds which enter the control equipment are recovered or
destroyed, and that overall VOC emissions do not exceed the solids equivalent
limit of 2.21 pounds VOC per gallon of coating solids stated in paragraph 1. of
this subsection. |
|
| 3. |
For
the purpose of this subsection, the following definitions apply:
| (i) |
"Wire Coating" means the process of
applying a coating of electrically insulating varnish or enamel to aluminum or
copper wire for use in electrical machinery. |
|
|
| (bb) |
Petroleum Liquid Storage.
| 1. |
No person shall cause, let, permit,
suffer, or allow the use of a fixed roof storage vessel with capacities of
40,000 gallons or greater containing a volatile petroleum liquid where true
vapor pressure is greater than 1.52 psia unless:
| (i) |
the vessel has been fitted with a
floating roof; or |
| (ii) |
the vessel
has been fitted with control equipment demonstrated to have control efficiency
equivalent to or greater than required in (i) of this paragraph, and approved
by the Director. |
|
| 2. |
The
requirements of this subsection shall not apply to vessels:
| (i) |
underground, if the total volume of
petroleum liquids added to and taken from the tank annually does not exceed
twice the volume of the tank; or |
| (ii) |
having capacities less than 425,000
gallons used to store crude oil prior to lease custody transfer. |
|
| 3. |
For the purpose of this
subsection, the following definitions shall apply:
| (i) |
"Crude Oil" means a naturally occurring
mixture which consists of hydrocarbons and/or sulfur, nitrogen and/or oxygen
derivatives of hydrocarbons and which is a liquid at standard
conditions; |
| (ii) |
"Floating Roof"
means a storage vessel cover consisting of a double deck, pontoon single deck,
internal floating cover or covered floating roof, which rests upon and is
supported by the petroleum liquid being contained, and is equipped with a
closure seal or seals to close the space between the roof edge and tank
wall; |
| (iii) |
"Petroleum Liquids"
means crude oil, condensate, and any finished or intermediate products
manufactured in a petroleum refinery; |
| (iv) |
"Petroleum Refinery" means any facility
engaged in producing gasoline, kerosene, distillate fuel oils, residual fuel
oils, lubricants, or other products through distillation of crude oils, or
through redistillation, cracking, extraction, or reforming of unfinished
petroleum derivatives; |
| (v) |
"True
Vapor Pressure" means the equilibrium partial pressure exerted by a petroleum
liquid as determined in accordance with methods described in American Petroleum
Institute Bulletin 2517, "Evaporation Loss from Floating Roof Tanks,"
1962. |
|
|
| (cc) |
Bulk Gasoline Terminals.
| 1. |
No
person may load gasoline into any tank trucks or trailers from any bulk
gasoline terminal unless:
| (i) |
The bulk
gasoline terminal is equipped with vapor control equipment capable of complying
with subparagraph 1.(v) of this paragraph 1., properly installed, in good
working order, in operation, and consisting of one of the following:
| (I) |
An adsorber or condensation equipment
which processes and recovers at least 90 percent of all vapors and gases from
the equipment being controlled; or |
| (II) |
Vapor collection equipment which directs
all vapors to a fuel gas system; or |
| (III) |
Control equipment demonstrated to have
control efficiency equivalent to or greater than required in (I) or (II) of
this paragraph, and approved by the Director; and |
|
| (ii) |
All displaced vapors and gases are
vented only to the vapor control equipment; and |
| (iii) |
Complete drainage of any loading arm
will be accomplished before it is removed from the tank; and |
| (iv) |
All loading and vapor lines are equipped
with fittings which make vapor-tight connections and which close automatically
when disconnected, or a loading arm with vapor return line and hatch seal
designed to prevent the escape of gases and vapor while loading; |
| (v) |
Sources and persons affected under this
subsection may not allow mass emissions of volatile organic compounds from
control equipment to exceed 4.7 grains per gallon of gasoline loaded. |
|
| 2. |
Sources and persons affected
under this subsection shall comply with the vapor collection and control system
requirements of Rule 3913-1-.02(2)(ss). |
| 3. |
The requirements of this subsection shall
not apply to loading of gasoline into tank trucks or trailers of less than 3000
gallons capacity outside those counties of Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Fulton, Gwinnett, Henry, Paulding, and Rockdale. |
| 4. |
The requirements of this subsection shall
apply to loading of gasoline into tank trucks or trailers of less than 3000
gallons capacity inside those counties of Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Fulton, Gwinnett, Henry, Paulding, and Rockdale after July 1,
1991. |
| 5. |
For the purpose of this
subsection, the following definitions apply:
| (i) |
"Bulk Gasoline Terminal" means a gasoline
storage facility which receives gasoline from refineries primarily by pipeline,
ship, or barge, and delivers gasoline to bulk gasoline plants or to commercial
or retail accounts primarily by tank truck and has an average daily throughput
of more than 20,000 gallons of gasoline. |
| (ii) |
"Gasoline" means a petroleum distillate
having a Reid vapor pressure of 4 psia or greater. |
|
|
| (dd) |
Cutback Asphalt.
| 1. |
After January 1, 1981, no person may
cause, allow or permit the use of cutback asphalts for paving purposes except
as necessary for:
| (i) |
long-life stockpile
storage; or |
| (ii) |
the use or
application at ambient temperatures less than 50°F; or |
| (iii) |
solely as a penetrating prime coat;
or |
|
| 2. |
For the
purpose of this subsection, the following definitions shall apply:
| (i) |
"Asphalt" means a dark-brown to black
cementitious material (solid, semisolid, or liquid in consistency) in which the
predominating constituents are bitumens which occur in nature as such or which
are obtained as residue in refining petroleum; |
| (ii) |
"Cutback Asphalt" means asphalt cement
which has been liquified by blending with petroleum solvents (diluents). Upon
exposure to atmospheric conditions the diluents evaporate, leaving the asphalt
cement to perform its function; |
| (iii) |
"Penetrating Prime Coat" means an
application of low viscosity liquid asphalt to an absorbent surface. It is used
to prepare an untreated base for an asphalt surface. The prime penetrates the
base and plugs the voids, hardens the top, and helps bind it to the overlying
asphalt course. It also reduces the necessity of maintaining an untreated base
course prior to placing the asphalt pavement. |
|
|
| (ee) |
Petroleum Refinery.
| 1. |
Persons responsible for any vacuum
producing system at a petroleum refinery shall control the emissions of any
noncondensable volatile organic compound from the condensers, hot wells or
accumulators by:
| (i) |
Piping the noncondensable
vapors to a firebox or incinerator; or |
| (ii) |
Compressing the vapors and adding them
to the refinery fuel gas; or |
| (iii) |
Controlling the vapors by using control equipment demonstrated to have control
efficiency equivalent to or greater than required in (i) or (ii) of this
paragraph, and approved by the Director; and |
|
| 2. |
Persons responsible for any wastewater
(oil/water) separator at a petroleum refinery shall:
| (i) |
Provide covers and seals approved by the
Director, on all separators and forebays; and |
| (ii) |
Equip all openings in covers,
separators, and forebays with lids or seals such that the lids or seals are in
the closed position at all times except when in actual use. |
|
| 3. |
Before January 1, 1980, the
owner or operator of any affected petroleum refinery located in this State
shall develop and submit to the Director for approval a detailed procedure for
minimization of volatile organic compound emissions during process unit
turnaround. As a minimum, the procedure shall provide for:
| (i) |
Depressurization venting of the process
unit or vessel to a vapor recovery system, flare or firebox; and |
| (ii) |
No emission of volatile organic
compounds from a process unit or vessel unless its internal pressure is 19.7
psi or less. |
|
| 4. |
For the
purpose of this subsection, the following definitions shall apply:
| (i) |
"Accumulator" means the reservoir of a
condensing unit receiving the condensate from the condenser; |
| (ii) |
"Condenser" means any heat transfer
device used to liquefy vapors by removing their latent heats of vaporization.
Such devices include, but are not limited to, shell and tube, coil, surface, or
contact condensers; |
| (iii) |
"Firebox"
means the chamber or compartment of a boiler or furnace in which materials are
burned but does not mean the combustion chamber of an incinerator; |
| (iv) |
"Forebays" means the primary sections of
a wastewater separator; |
| (v) |
"Hot
Well" means the reservoir of a condensing unit receiving the warm condensate
from the condenser; |
| (vi) |
"Petroleum
Refinery" means any facility engaged in producing gasoline, kerosene,
distillate fuel oils, residual fuel oils, lubricants, or other products through
distillation, cracking, extraction, or refining of unfinished petroleum
derivatives; |
| (vii) |
"Refinery Fuel
Gas" means any gas which is generated by a petroleum refinery process unit and
which is combusted, including any gaseous mixture of natural gas and fuel
gas; |
| (viii) |
"Turnaround" means the
procedure of shutting a refinery unit down after a run to do necessary
maintenance and repair work and putting the unit back on stream; |
| (ix) |
"Vacuum Producing System" means any
reciprocating, rotary, or centrifugal blower or compressor, or any jet ejector
or device that takes suction from a pressure below atmospheric and discharges
against atmospheric pressure; |
| (x) |
"Vapor Recovery System" means a system that prevents releases to the
atmospheric of no less than 90 percent by weight of organic compounds emitted
during the operation of any transfer, storage, or process equipment; |
| (xi) |
"Wastewater (oil/water) Separator" means
any device or piece of equipment which utilizes the difference in density
between oil and water to remove oil and associated chemicals from water or any
device, such as a flocculation tank, clarifier, etc., which removes petroleum
derived compounds from wastewater. |
|
|
| (ff) |
Solvent Metal Cleaning.
| 1. |
No person shall cause, suffer, allow, or
permit the operation of a cold cleaner degreaser unless the following
requirements for control of emissions of the volatile organic compounds are
satisfied:
| (i) |
The degreaser shall be equipped
with a cover to prevent the escape of volatile organic compounds during periods
of non-use; |
| (ii) |
The degreaser
shall be equipped with a facility for draining cleaned parts before
removal; |
| (iii) |
If used, the solvent
spray must be a solid, fluid stream (not a fine, atomized or shower type spray)
and at a pressure which does not cause excessive splashing; |
| (iv) |
If the solvent volatility is 0.60 psi or
greater measured at 100°F, or if the solvent is heated above 120oF, then
one of the following control devices must be used:
| (I) |
Freeboard that gives a freeboard ratio of
0.7 or greater; |
| (II) |
Water cover
(solvent must be insoluble in and heavier than water); |
| (III) |
Other systems of equivalent control,
such as a refrigerated chiller or carbon adsorption. |
|
| (v) |
Waste solvent shall be stored only in
covered containers and shall not be disposed of by such a method as to allow
excessive evaporation into the atmosphere. |
|
| 2. |
No person shall cause, suffer, allow, or
permit the operation of an open top vapor degreaser unless the following
requirements for control of emissions of volatile organic compounds are
satisfied:
| (i) |
The degreaser shall be equipped
with a cover to prevent the escape of volatile organic compounds during periods
of non-use; |
| (ii) |
The degreaser
shall be equipped with one of the following control devices:
| (I) |
Freeboard ratio greater than or equal to
0.75; |
| (II) |
Refrigerated
chiller; |
| (III) |
Enclosed design
(cover or door opens only when the dry part is actually entering or exiting the
degreaser); |
| (IV) |
Carbon adsorption
system, with ventilation greater than 50 cfm/ft2 of
air/vapor area (when cover is open), and exhausting less than 25 ppm solvent
averaged over one complete adsorption cycle; or |
| (V) |
Control equipment demonstrated to have
control efficiency equivalent to or better than any of the above. |
|
| (iii) |
The degreaser shall be
operated in accordance with the following procedures. Operating instructions
summarizing these procedures shall be displayed on the degreaser.
| (I) |
Keep cover closed at all times except
when processing work loads through the degreaser; |
| (II) |
Minimize solvent carry-out by the
following measures:
| I. |
Rack parts to allow
full drainage; |
| II. |
Degrease the
work load in the vapor zone at least 30 seconds or until condensation
ceases; |
| III. |
Tip out any pools of
solvent on the cleaned parts before removal; |
| IV. |
Allow parts to dry within the degreaser
for at least 15 seconds or until visually dry. |
|
| (III) |
Do not degrease porous or adsorbent
materials, such as cloth, leather, wood or rope; |
| (IV) |
Work loads should not occupy more than
half of the degreaser's open top area; |
| (V) |
The vapor level should not drop more than
4 inches when the workload enters the vapor zone; |
| (VI) |
Never spray above the vapor
level; |
| (VII) |
Repair solvent leaks
immediately, or shutdown the degreaser; |
| (VIII) |
Ventilation fans should not be used
near the degreaser opening; |
| (IX) |
Water should not be visually detectable in solvent exiting the water
separator. |
|
| (iv) |
Waste
solvent shall be stored only in covered containers and shall not be disposed of
or transferred to another party by such a method as to allow excessive
evaporation into the atmosphere. |
|
| 3. |
No person shall cause, suffer, allow, or
permit the operation of a conveyorized degreaser unless the following
requirements for control of emissions of the volatile organic compounds are
satisfied.
| (i) |
The degreaser shall be equipped
with a cover to prevent the escape of volatile organic compounds during periods
of non-use; |
| (ii) |
The degreaser
shall be equipped with either a drying tunnel, or other means such as rotating
(tumbling) basket, sufficient to prevent cleaned parts from carrying out
solvent liquid or vapor; |
| (iii) |
The
degreaser shall be equipped with one of the following:
| (I) |
Refrigerated chiller; |
| (II) |
Carbon adsorption system, with
ventilation greater than 50 cfm/ft2 of air/vapor
area (when down-time covers are open), and exhausting less than 25 ppm of
solvent by volume averaged over a complete adsorption cycle; or |
| (III) |
Control equipment demonstrated to have
control efficiency equivalent to or better than any of the above. |
|
| (iv) |
The degreaser shall be
operated in accordance with the following procedure. Operating instructions
summarizing these procedures shall be displayed on the degreaser.
| (I) |
Exhaust ventilation should not exceed 65
cfm per ft2 of degreaser opening, unless necessary
to meet OSHA requirements. Work place fans should not be used near the
degreaser opening; |
| (II) |
Minimize
carryout emissions by:
| I. |
Racking parts for
best drainage; Maintaining vertical conveyor speed at less than 11
ft/min. |
|
| (III) |
Repair
solvent leaks immediately, or shutdown the degreaser; |
| (IV) |
Water should not visibly be detectable
in the solvent exiting the water separator; |
| (V) |
Down-time cover must be placed over
entrances and exits of conveyorized degreasers immediately after the conveyor
and exhaust are shutdown and removed just before they are started
up. |
|
| (v) |
Waste solvent
shall be stored only in covered containers and shall not be disposed of or
transferred to another party by such a method as to allow excessive evaporation
into the atmosphere. |
|
| 4. |
The following requirements apply to degreasers using trichloroethylene, carbon
tetrachloride, and/or chloroform in a total concentration greater than 5
percent by weight:
| (i) |
Degreasers constructed
or reconstructed after November 29, 1993 shall comply with paragraph
391-3-1-.02(9)(b)34. "Emission Standard for Halogenated Solvent Cleaning, 40
CFR 63, Subpart T, as amended" (NESHAP) and not paragraphs 1. through 3. of
this subsection (ff) (Georgia Rule). |
| (ii) |
Existing degreasers (constructed or
reconstructed on or before November 29, 1993) shall comply with paragraphs 1.
through 3.of this subsection (ff) (Georgia Rule) until December 2, 1997; after
which they must comply with paragraph 391-3-1-.02(9)(b)34.(NESHAP). |
| (iii) |
An existing degreaser (as defined
above) may elect to comply with paragraph 391-3-1-.02(9)(b)34. prior to
December 2, 1997. In such case, they are not required comply with Paragraphs 1.
through 3. of this subsection (ff) (Georgia Rule) once they are in compliance
with paragraph 391-3-1-.02(9)(b)34.(NESHAP). |
| (iv) |
Any facility which currently complies
with paragraphs 391-3-1-.02(2)(ff)1. through 3. (Georgia Rule) which will be
changing to comply with paragraph 391-3-1-.02(9)(b)34. (NESHAP) should submit a
schedule of construction/ modification for changes necessary to comply with
391-3-1-.02(9)(b)34. (NESHAP) as soon as practically possible but no later than
60 days prior to any construction/modification. |
|
| 5. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Cold
Cleaning" means the batch process of cleaning and removing soils from metal
surfaces by spraying, brushing, flushing or immersion while maintaining the
solvent below its boiling point. Wipe cleaning is not included in this
definition; |
| (ii) |
"Conveyorized
Degreasing" means the continuous process of cleaning and removing soils from
metal surfaces by operating with either cold or vaporized solvents; |
| (iii) |
"Freeboard Height" means the distance
from the top of vapor zone to the top of the degreaser tank; |
| (iv) |
"Freeboard Ratio" means the freeboard
height divided by the width (smallest dimension) of the degreaser; |
| (v) |
"Open Top Vapor Degreasing" means the
batch process of cleaning and removing soils from metal surfaces by condensing
hot solvent vapor on the colder metal parts; |
| (vi) |
"Solvent Metal Cleaning" means the
process of cleaning soils from metal surfaces by cold cleaning, or open top
vapor degreasing or conveyorized degreasing. Solvent metal cleaning does not
include cleaners that use aqueous cleaning solvent or buckets, pails and
beakers with capacities of two gallons or less. |
| (vii) |
"Aqueous Cleaning Solvent" means a
cleaning solvent in which water is the primary ingredient (greater than 80
percent by weight of cleaning solvent solution as applied must be
water). |
|
| 6. |
The
requirements of this subsection shall not apply to any solvent metal cleaning
operation subject to Section 391-3-1-.02(2)(kkk) of the Georgia Rules for Air
Quality Control "VOC Emissions from Aerospace manufacturing and Rework
Facilities." |
|
| (gg) |
Kraft Pulp Mills.
| 1. |
Except as provided
for in paragraph 2. of this subsection, no person shall cause, let, suffer,
permit, or allow the emissions of TRS from any kraft pulp mill in operation, or
under construction contract, on or before September 24, 1976, in amounts equal
to or exceeding the following:
| (i) |
Recovery
Furnaces.
| (I) |
Old Recovery Furnaces: 20 parts
per million of TRS on a dry basis and as a 24-hour average, corrected to 8
volume percent oxygen; |
| (II) |
New
Recovery Furnaces: 5 parts per million of TRS on a dry basis and as a 24-hour
average, corrected to 8 volume percent oxygen; |
| (III) |
Cross Recovery Furnaces: 25 parts per
million of TRS on a dry basis and as a 24-hour average, corrected to 8 volume
percent oxygen. |
|
| (ii) |
Digester System or Multiple-Effect Evaporator System: 5 parts per million of
TRS on a dry basis and a 24-hour average, corrected to 10 volume percent oxygen
unless the following conditions are met:
| (I) |
The gases are combusted in a lime kiln subject to the provisions of paragraph
(iv) of this subsection; or |
| (II) |
The gases are combusted in a recovery furnace subject to the provisions of
paragraph (i) of this subsection; or |
| (III) |
The gases are combusted with other
gases in an incinerator or other device, or combusted in a lime kiln or
recovery boiler not subject to the provisions of this subsection, and are
subjected to a minimum temperature of 1200°F for at least 0.5 second;
or |
| (IV) |
The gases are controlled by
a means other than combustion. In this case, the gases discharged shall not
contain TRS in excess of five parts per million on a dry basis and as a 24-hour
average, corrected to the actual oxygen content of the untreated gas
stream. |
|
| (iii) |
Smelt
Dissolving Tanks: 0.0168 pounds of TRS per ton of black liquor solids (dry
weight). |
| (iv) |
Lime Kilns: 40 parts
per million of TRS on a dry basis and as a 24-hour average, corrected to 10
volume percent oxygen. |
|
| 2. |
Nothing in paragraph 1. shall prevent the owner or operator of a kraft pulp
mill subject to the provisions of this subsection (gg) from applying to the
Director for permission to control TRS emissions from the kraft pulp mill under
the provisions of this paragraph provided that:
| (i) |
General Provisions.
| (I) |
The owner or operator of such kraft pulp
mill makes such application in writing no later than six months following the
notification date; and |
| (II) |
In the
event that the kraft pulp mill contains TRS emitting process equipment which is
subject to the New Source Performance Standard for Kraft Pulp Mills,
391-3-1-.02(2)(b)23., then that TRS emitting process equipment must also comply
with the applicable New Source Performance Standard TRS emission
limitation(s); |
| (III) |
The owner or
operator of such kraft pulp mill may not elect to control TRS emissions from
process equipment not subject to the provisions of this subsection (gg) in lieu
of controlling TRS emissions from those sources subject to this subsection
(gg); and |
| (IV) |
For the purpose of
this paragraph 2.; the maximum allowable emissions of TRS shall be calculated
using the production rate (annual average or most recent 12 months of record)
for the kraft pulp mill expressed as tons of air dried pulp per day, and the
allowable emission rate of TRS from the kraft pulp mill shall be expressed as
pounds of TRS per ton of air dried pulp. |
| (V) |
For the purpose of this paragraph, the
"notification date" means September 1, 1988. |
|
| (ii) |
Emission Limitation: No person shall
cause, let, suffer, permit, or allow the total emissions of TRS from the
following processes: recovery furnace(s), lime kiln(s), smelt dissolving
tank(s), digester system, multiple-effect evaporator system, equal to or
exceeding the amount determined by the following formula:
A = RB + LK + 0.065 pounds of TRS per ton of air dried
pulp;
The values for the terms RB and LK shall be determined using
the following formula:
Where:
A = the total amount of allowable TRS emissions from the
kraft pulp mill expressed as pounds of TRS per ton of air dried pulp;
LK = the fraction of the total allowable emission of TRS in
pounds per ton of air dried pulp for lime kilns;
RB = the fraction of the total allowable emission of TRS in
pounds per ton of air dried pulp for recovery furnaces;
U = tons per hour of lime mud solids calcined in lime kiln(s)
not subject to the New Source Performance Standard for Kraft Pulp Mills;
V = tons per hour of lime solids calcined in lime kiln(s)
subject to the New Source Performance Standard for Kraft Pulp Mills;
W = pounds per hour of black liquor solids burned in recovery
furnace(s) subject to the New Source Performance Standard for Kraft Pulp
Mills;
X = pounds per hour of black liquor solids burned in new
recovery furnace(s);
Y = pounds per hour of black liquor solids burned in old
recovery furnace(s);
Z = pounds per hour of black liquor solids burned in cross
recovery furnace(s);
|
|
| 3. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"New
Recovery Furnace" means a recovery furnace which had stated in the purchase
contract a TRS performance guarantee or which included in the purchase contract
a statement that the control of air pollutants was a design objective and which
has incorporated into its design: membrane wall or welded wall construction;
and emission control air systems. |
| (ii) |
"Old Recovery Furnace" means a recovery
furnace which is not classified as a new recovery furnace. |
|
|
| (hh) |
Petroleum Refinery
Equipment Leaks.
| 1. |
No person shall
cause, let, suffer, or allow the use of petroleum refinery equipment unless:
| (i) |
A plan is submitted to the Director by no
later than July 1, 1981 for monitoring VOC leaks. Such a program must contain:
| (I) |
A list of refinery units and the quarter
in which they will be monitored; |
| (II) |
A copy of the log book format; |
| (III) |
The make and model of the monitoring
equipment to be used. |
|
| (ii) |
Monitoring for potential VOC leaks is
carried out no less frequently than:
| (I) |
Yearly using detection equipment for pump seals, pipeline valves in liquid
service, and process drains; |
| (II) |
Quarterly using detection equipment for compressor seals, pipeline valves in
gaseous service, and pressure relief valves in gaseous service; |
| (III) |
Weekly by visible inspection for all
pump seals; |
| (IV) |
Immediately using
detection equipment for any pump seals from which liquids are observed dripping
and immediately after repair of any component previously found to be
leaking; |
| (V) |
Within 24 hours for a
relief valve after it has vented to the atmosphere. |
|
| (iii) |
All components which have emissions
with a VOC concentration exceeding 10,000 ppm, as determined by Method 21 of
the reference in Section 391-3-1-.02(3)(a) of these Rules, shall be affixed
with a weatherproof and readily visible tag, bearing an identification number
and the date on which the leak is located. This tag shall remain in place until
the leaking component is repaired. |
| (iv) |
Leaking components as defined by (iii)
above which can be repaired without a unit shutdown shall be repaired and
retested as soon as practicable but no later than 15 days after the leak is
identified. |
| (v) |
Leaking components
as defined by (iii) above which require unit shutdown for repair may be
corrected at the regularly scheduled turnaround unless the Director at his
discretion requires early unit turnaround based on the number and severity of
tagged leaks awaiting turnaround. |
| (vi) |
Except for safety pressure relief
valves, no owner or operator of a petroleum refinery shall install or operate a
valve at the end of a pipe or line containing volatile organic compounds unless
the pipe or line is sealed with a second value, a blind flange, a plug, or a
cap. The sealing device may be removed only when a sample is being taken or
during maintenance operations. |
| (vii) |
Pipeline valves and pressure relief
valves in gaseous volatile organic compound service shall be marked in some
manner that will be readily obvious to both refinery personnel performing
monitoring and the Director. |
| (viii) |
Pressure relief devices which are connected to an operation flare header, vapor
recovery device, inaccessible valves, storage tank valves, and valves that are
not externally regulated are exempt from the monitoring requirements of this
rule. |
|
| 2. |
The owner or
operator of a petroleum refinery shall maintain a leaking components monitoring
log. Copies of the monitoring log shall be retained by the owner or operator
for a minimum of two years after the date on which the record was made or the
report prepared and shall immediately be made available to the Director, upon
verbal or written request, at any reasonable time. The monitoring log shall
contain the following data:
| (i) |
The name and
the process unit where the component is located. |
| (ii) |
The type of component (e.g., valve,
seal). |
| (iii) |
The tag number of the
component. |
| (iv) |
The date on which a
leaking component is discovered. |
| (v) |
The date on which a leaking component is
repaired. |
| (vi) |
The date and
instrument reading of the recheck procedure after a leaking component is
repaired. |
| (vii) |
A record of the
calibration of the monitoring instrument. |
| (viii) |
Those leaks that cannot be repaired
until turnaround. |
| (ix) |
The total
number of components checked and the total number of components found
leaking. |
|
| 3. |
The owner or
operator of a petroleum refinery shall:
| (i) |
Submit a report to the Director by the fifteenth day of January, April, July,
and October that lists all leaking components that were located during the
previous three calendar months but not repaired within fifteen days, all
leaking components awaiting unit turnaround, the total number of components
inspected, and the total number of components found leaking. |
| (ii) |
Submit a signed statement with the
report attesting to the fact that, all monitoring and repairs were performed as
stipulated in the monitoring program. |
| (iii) |
The first quarterly report shall be
submitted to the Director no later than January 1, 1982. |
|
| 4. |
The Director, upon written notice, may
modify the monitoring, record keeping and reporting requirements. |
| 5. |
For the purpose of this subsection, the
following definitions apply:
| (i) |
"Petroleum
refinery" means any facility engaged in producing gasoline, aromatics,
kerosene, distillate fuel oils residual fuel oils, lubricants, asphalt, or
other products through distillation of petroleum or through redistillation,
cracking, rearrangement or reforming of unfinished petroleum
derivatives. |
| (ii) |
"Component" means
any piece of equipment which has the potential to leak volatile organic
compounds when tested in the manner described in subparagraph 1.(iii). These
sources include, but are not limited to, pumping seals, compressor seals, seal
oil degassing vents pipeline valves, pressure relief devices, process drains,
and open ended pipes. Excluded from these sources are valves which are not
externally regulated. |
| (iii) |
"Liquid
service" means equipment which processes, transfers or contains a volatile
organic compound or mixture of volatile organic compounds in the liquid
phase. |
| (iv) |
"Gas service" means
equipment which processes, transfers or contains a volatile organic compound or
mixture of volatile organic compounds in the gaseous phase. |
| (v) |
"Valves not externally regulated" means
valves that have no external controls, such as in-line check valves. |
| (vi) |
"Refinery unit" means a set of compounds
which are a part of a basic process operation, such as, distillation,
hydrotreating, cracking or reforming of hydrocarbons. |
|
|
| (ii) |
VOC Emissions from
Surface Coating of Miscellaneous Metal Parts and Products.
| 1. |
No person shall cause, let, permit,
suffer, or allow the emissions of VOC from surface coating of miscellaneous
metal parts and products to exceed:
| (i) |
4.3
pounds per gallon of coating, excluding water, delivered to a coating
applicator that applies clear coatings. If any coating delivered to the coating
applicator contains more than 4.3 pounds VOC per gallon, the solids equivalent
limit shall be 10.3 pounds VOC per gallon of coating solids delivered to the
coating applicator. |
| (ii) |
3.5 pounds
per gallon of coating, excluding water, delivered to a coating applicator in a
coating application system that is air dried or forced warm air dried at
temperatures up to 194°F. If any coating delivered to the coating
applicator contains more than 3.5 pounds VOC per gallon, the solids equivalent
limit shall be 6.67 pounds VOC per gallon of coating solids delivered to the
coating applicator. |
| (iii) |
3.5
pounds per gallon of coating, excluding water, delivered to a coating
applicator that applies extreme performance coatings. If any coating delivered
to the coating applicator contains more than 3.5 pounds VOC per gallon, the
solids equivalent limit shall be 6.67 pounds VOC per gallon of coating solids
delivered to the coating applicator. |
| (iv) |
6.2 pounds per gallon of coating,
excluding water, delivered to a coating applicator in a high performance
architectural coating operation; and |
| (v) |
3.0 pounds per gallon of coating,
excluding water, delivered to a coating applicator for all other coatings and
coating application systems. If any coating delivered to the coating applicator
contains more than 3.0 pounds VOC per gallon, the solids equivalent limit shall
be 5.06 pounds VOC per gallon of coating solids delivered to the coating
applicator. |
|
| 2. |
No person
shall cause, let, permit, suffer, or allow the emissions of VOC from surface
coating of miscellaneous metal parts and products using air-dried coatings to
exceed:
| (i) |
2.8 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies anyone of the
following air-dried coatings: general one component; general multi component;
military specification; drum coating - new exterior. If any coating delivered
to the coating applicator contains more than 2.8 pounds VOC per gallon, the
solids equivalent limit shall be 4.52 pounds VOC per gallon of coating solids
delivered to the coating applicator. |
| (ii) |
3.5 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies any one of the
following air-dried coatings: camouflage; electric-insulating varnish; etching
filler; high temperature; metallic; mold-seal; pan backing; pretreatment; drum
coating - new interior; drum coating - reconditioned, exterior; silicone
release; vacuum-metalizing; extreme high-gloss; extreme performance;
heat-resistant; drum coating - reconditioned interior; solar-absorbent;
prefabricated architectural multi-component; prefabricated architectural
one-component. If any coating delivered to the coating applicator contains more
than 3.5 pounds VOC per gallon, the solids equivalent limit shall be 6.67
pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (iii) |
3.5 pounds per
gallon of coating, excluding water, delivered to a coating applicator that
applies the following air-dried coating: repair and touch-up. |
| (iv) |
6.2 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies the following
air-dried coating: high performance architectural. |
|
| 3. |
No person shall cause, let, permit,
suffer, or allow the emissions of VOC from surface coating of miscellaneous
metal parts and products using baked coatings to exceed:
| (i) |
2.3 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies anyone of the
following baked coatings: general one component; general multi-component;
military specification; prefabricated architectural multi-component;
prefabricated architectural one-component. If any coating delivered to the
coating applicator contains more than 2.3 pounds VOC per gallon, the solids
equivalent limit shall be 3.35 pounds VOC per gallon of coating solids
delivered to the coating applicator. |
| (ii) |
2.8 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies drum coating -
new exterior coating. If any coating delivered to the coating applicator
contains more than 2.8 pounds VOC per gallon, the solids equivalent limit shall
be 4.52 pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (iii) |
3.0 pounds per
gallon of coating, excluding water, delivered to a coating applicator that
applies anyone of the following baked coatings: drum coating - reconditioned
interior; camouflage; electric-insulating varnish; etching filler; extreme
high-gloss; extreme performance; heat-resistant; high temperature; metallic;
mold-seal; pan backing; pretreatment; drum coating - new interior; drum coating
- reconditioned exterior; silicone release; solar-absorbent; and
vacuum-metalizing. If any coating delivered to the coating applicator contains
more than 3.0 pounds VOC per gallon, the solids equivalent limit shall be 5.06
pounds VOC per gallon of coating solids delivered to the coating
applicator. |
| (iv) |
6.2 pounds per
gallon of coating, excluding water, delivered to a coating applicator that
applies the following baked coating: high performance architectural. |
| (v) |
3.0 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies repair and
touch-up coatings. |
|
| 4. |
No
person shall cause, let, permit, suffer, or allow the emissions of VOC from
surface coating of motor vehicle materials at a facility that is not an
automobile or light-duty truck manufacturing facility to exceed:
| (i) |
1.7 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies the following
motor vehicle materials: gasket/gasket sealing material and bedliner. |
| (ii) |
3.5 pounds per gallon of coating,
excluding water, delivered to a coating applicator that applies the following
motor vehicle materials: cavity wax, sealer, deadener, underbody coating, trunk
interior coating, and lubricating wax/compound. |
|
| 5. |
If more than one emission limitation in
this subparagraph (ii) applies to a specific coating, then the least stringent
emission limitation in this subparagraph (ii) of this subsection shall be
applied. |
| 6. |
All VOC emissions from
solvent washings shall be considered in the emission limitations unless the
solvent is directed into containers that prevent evaporation into the
atmosphere. |
| 7. |
The emission limits
in this subsection shall be achieved by:
| (i) |
the application of low solvent coating technology where each and every coating
meets the limit expressed in pounds VOC per gallon of coating, excluding water,
stated in paragraphs 1., 2., 3., and 4. of this subsection; or |
| (ii) |
the application of low solvent coating
technology where the 24-hour weighted average of all coatings on a single
coating line or operation meets the solids equivalent limit expressed in pounds
VOC per gallon of coating solids, stated in paragraphs 1.,2., and 3. of this
subsection; averaging across lines is not allowed; or |
| (iii) |
control equipment, including but not
limited to incineration, carbon adsorption and condensation, with a capture
system approved by the Director, provided that 90 percent of the nonmethane
volatile organic compounds which enter the control equipment are recovered or
destroyed, and that overall VOC emissions do not exceed the solids equivalent
limit, expressed in pounds VOC per gallon of coating solids stated in
paragraphs 1.,2., 3., and 4. of this subsection. |
| (iv) |
for high performance architectural
coatings, compliance may be achieved only as stated in subparagraph 7.(i) or
7.(iii). There is no solids equivalent limit for such coatings. |
| (v) |
for motor vehicle materials, compliance
may be achieved only as stated in subparagraph 7.(i). There is no solids
equivalent limit for such coatings. |
| (vi) |
for repair and touch-up materials,
compliance may be achieved only as stated in subparagraphs 7.(i). There is no
solids equivalent limit for such coatings. |
|
| 8. |
For the purpose of this subsection, the
following definitions apply:
| (i) |
"Air dried
coating" means coatings which are dried by the use of air or forced warm air at
temperatures up to 194°F. |
| (ii) |
"Baked coating" means a coating that is cured at a temperature at or above
194°F. |
| (iii) |
"Bedliner" means a
multi-component coating, used at a facility that is not an automobile or
light-duty truck assembly coating facility, applied to a cargo bed after the
application of topcoat to provide additional durability and chip
resistance. |
| (iv) |
"Cavity wax" means
a coating, used at a facility that is not an automobile or light-duty truck
assembly coating facility, applied into the cavities of the vehicle primarily
for the purpose of enhancing corrosion protection. |
| (v) |
"Camouflage coating" means a coating
used, principally by the military, to conceal equipment from
detection. |
| (vi) |
"Clear coating"
means a colorless coating which contains binders, but no pigment, and is
formulated to form a transparent film. |
| (vii) |
"Coating application system" means all
operations and equipment which applies, conveys, and dries a surface coating,
including, but not limited to spray booths, flow coaters, flashoff areas, air
dryers and ovens. |
| (viii) |
"Deadener"
means a coating, used at a facility that is not an automobile or light-duty
truck assembly coating facility, applied to selected vehicle surfaces primarily
for the purpose of reducing the source of road noise in the passenger
compartment. |
| (ix) |
"Drum" means any
cylindrical metal shipping container larger than 12 gallons capacity but no
larger than 110 gallons capacity. |
| (x) |
"Electric dissipating coating" means a
coating that rapidly dissipates a high-voltage electric charge. |
| (xi) |
"Electric-insulating varnish" means a
non-convertible-type coating applied to electric motors, components of electric
motors, or power transformers, to provide electrical, mechanical, and
environmental protection or resistance. |
| (xii) |
"EMI/RFI Shielding" means a coating
used on electrical or electronic equipment to provide shielding against
electromagnetic interference, radio frequency interference, or static
discharge. |
| (xiii) |
"Etching filler"
means a coating that contains less than 23 percent solids by weight, at least
0.5 percent acid by weight, and is used instead of applying a pretreatment
coating followed by a primer. |
| (xiv) |
"Extreme high-gloss coating" means a coating which, when tested by the American
Society for Testing Material Test Method D-523 adopted in 1980, shows a
reflectance of 75 or more on a 60 degree meter. |
| (xv) |
"Extreme-performance coating" means a
coating used on a metal or plastic surface where the coated surface is, in its
intended use, subject to the following: (a) Chronic exposure to corrosive,
caustic or acidic agents, chemicals, chemical fumes, chemical mixtures or
solutions; or (b) Repeated exposure to temperatures in excess of 250°F; or
(c) Repeated heavy abrasion, including mechanical wear and repeated scrubbing
with industrial grade solvents, cleansers or scouring agents. Extreme
performance coatings include, but are not limited to, coatings applied to
locomotives, railroad cars, farm machinery, and heavy duty trucks. |
| (xvi) |
"Extreme environmental conditions"
means exposure to any of: the weather all of the time, temperatures
consistently above 200°F, detergents, abrasive and scouring agents,
solvents, corrosive atmospheres, or similar environmental conditions; |
| (xvii) |
"Gasket/sealing material" means a
fluid, used at a facility that is not an automobile or light-duty truck
assembly coating facility, applied to coat a gasket or replace and perform the
same function as a gasket. Automobile and light-duty truck gasket/gasket
sealing material includes room temperature vulcanization (RTV) seal
material. |
| (xviii) |
"Heat-resistant
coating" means a coating that must withstand a temperature of at least
400°F during normal use. |
| (xix) |
"High-performance architectural coating" means a coating used to protect
architectural subsections and which meets the requirements of the Architectural
Aluminum Manufacturer Association's publication number AAMA 2604-05 (Voluntary
Specification, Performance Requirements and Test Procedures for High
Performance Organic Coatings on Aluminum Extrusions and Panels) or 2605-05
(Voluntary Specification, Performance Requirements and Test Procedures for
Superior Performing Organic Coatings on Aluminum Extrusions and
Panels). |
| (xx) |
"High-temperature
coating" means a coating that is certified to withstand a temperature of
1000°F for 24 hours. |
| (xxi) |
"Low
solvent coating" means coatings which contain less organic solvent than the
conventional coatings used by the industry. Low solvent coatings include
water-borne, higher solids, electrodeposition and powder coatings. |
| (xxii) |
"Lubricating wax/compound" means a
protective lubricating material, used at a facility that is not an automobile
or light-duty truck assembly coating facility, applied to vehicle hubs and
hinges. |
| (xxiii) |
"Mask coating"
means thin film coating applied through a template to coat a small portion of a
substrate. |
| (xxiv) |
"Metallic
coating" means a coating which contains more than five grams of metal particles
per liter of coating as applied. "Metal particles" are pieces of a pure
elemental metal or combination of elemental metals. |
| (xxv) |
"Miscellaneous metal parts and
products" means surface coating of products manufactured by the following
industrial source categories: large farm machinery, small farm machinery, small
appliances, commercial machinery, industrial machinery, fabricated metal
products and any other industrial category which coats metal parts or products
under the Standard Industry Classification Code Major Groups 33, 34, 35, 36,
37, 38, 40, and 41. The miscellaneous metal parts and products source category
does not include:
| (I) |
automobiles and
light-duty trucks; |
| (III) |
flat metal sheets and
strips in the form of rolls or coils; |
| (IV) |
magnet wire for use in electrical
machinery; |
| (VII) |
aerospace
manufacturing and rework operations; |
| (VIII) |
automobile refinishing; |
| (IX) |
customized top coating of automobiles
and trucks, if production is less than 35 vehicles per day; and |
| (X) |
exterior of marine vessels. |
|
| (xxvi) |
"Military specification
coating" means a coating which has a formulation approved by a United States
Military Agency for use on military equipment. |
| (xxvii) |
"Mold seal coating" means the initial
coating applied to a new mold or a repaired mold to provide a smooth surface
which, when coated with a mold release coating, prevents products from sticking
to the mold. |
| (xxviii) |
"Multi-colored coating" means a coating which exhibits more than one color when
applied, and which means packaged in a single container and applied in a single
coat. |
| (xxix) |
"Multi-component
coating" means a coating requiring the addition of a separate reactive resin,
commonly known as a catalyst or hardener, before application to form an
acceptable dry film. |
| (xxx) |
"One-component coating" means a coating that is ready for application as it
comes out of its container to form an acceptable dry film. A thinner, necessary
to reduce the viscosity, is not considered a component. |
| (xxxi) |
"Optical coating" means a coating
applied to an optical lens. |
| (xxxii) |
"Pan-backing coating" means a coating applied to the surface of pots, pans, or
other cooking implements that are exposed directly to a flame or other heating
elements. |
| (xxxiii) |
"Prefabricated
architectural component coatings" are coatings applied to metal parts and
products which are to be used as an architectural structure. |
| (xxxiv) |
"Pretreatment coating" means a
coating which contains no more than 12 percent solids by weight, and at least
0.5 percent acid by weight, is used to provide surface etching, and is applied
directly to metal surfaces to provide corrosion resistance, adhesion, and ease
of stripping. |
| (xxxv) |
"Prime coat"
means the first of two or more films of coating applied to a metal
surface. |
| (xxxvi) |
"Repair coating"
means a coating used to re-coat portions of a previously coated product which
has sustained mechanical damage to the coating following normal coating
operations. |
| (xxxvii) |
"Sealer" means
a high viscosity material, used at a facility that is not an automobile or
light-duty truck assembly coating facility, generally, but not always, applied
in the paint shop after the body has received an electrodeposition primer
coating and before the application of subsequent coatings (e.g.,
primer-surfacer). The primary purpose of automobile and light-duty truck sealer
is to fill body joints completely so that there is no intrusion of water, gases
or corrosive materials into the passenger area of the body compartment. Such
materials are also referred to as sealant, sealant primer, or caulk. |
| (xxxviii) |
"Shock-free coating" means a
coating applied to electrical components to protect the user from electric
shock. The coating has characteristics of being of low capacitance and high
resistance, and having resistance to breaking down under high
voltage. |
| (xxxix) |
"Silicone-release
coating" means any coating which contains silicone resin and is intended to
prevent food from sticking to metal surfaces such as baking pans. |
| (xl) |
"Single coat" means one film of coating
applied to a metal surface. |
| (xli) |
"Solar-absorbent coating" means a coating which has as its prime purpose the
absorption of solar radiation. |
| (xlii) |
"Stencil coating" means an ink or a
pigmented coating which is rolled or brushed onto a template or stamp in order
to add identifying letters, symbols and/or numbers. |
| (xliii) |
"Topcoat" means the final film or
series of films of coating applied in a two-coat or more operation. |
| (xliv) |
"Touch-up coating" means a coating
used to cover minor coating imperfections appearing after the main coating
operation. |
| (xlv) |
"Translucent
coating" means a coating which contains binders and pigment and is formulated
to form a colored, but no opaque, film. |
| (xlvi) |
"Transfer efficiency" means the weight
(or volume) of coating solids adhering to the surface being coated divided by
the total weight (or volume) of coating solids delivered to the
applicator. |
| (xlvii) |
"Trunk interior
coating" means a coating, used at a facility that is not an automobile or
light-duty truck assembly coating facility, applied to the trunk interior to
provide chip protection. |
| (xlviii) |
"Two-component coating" means a coating requiring the addition of a separate
reactive resin, commonly known as a catalyst, before application to form an
acceptable dry film. |
| (xlix) |
"Underbody coating" means a coating, used at a facility that is not an
automobile or light-duty truck assembly coating facility, applied to the
undercarriage or firewall to prevent corrosion and/or provide chip protection.
|
| (l) |
"Vacuum-metalizing coating"
means the undercoat applied to the substrate on which the metal is deposited or
the overcoat applied directly to the metal film. Vacuum metalizing/physical
vapor deposition (PVD) is the process whereby metal is vaporized and deposited
on a substrate in a vacuum chamber. |
|
| 9. |
Applicability. Prior to January 1, 2015,
the requirements of this subparagraph (ii) shall apply to facilities at which
the potential emissions of volatile organic compounds from all surface coating
of miscellaneous parts and products equal or exceed 10 tons per year and are
located in Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Henry, Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 5., 6., 7., and 8. |
|
| 10. |
Applicability. Prior to
January 1, 2015, the requirements of this subparagraph (ii) shall apply to
facilities at which the potential emissions of volatile organic compounds from
all surface coating of miscellaneous parts and products equal or exceed 100
tons per year and are located outside the counties of Cherokee, Clayton, Cobb,
Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding,
and Rockdale as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 1., 5., 6., 7.,
and 8. |
|
| 11. |
Applicability.
On and after January 1, 2015, the requirements of this subparagraph (ii) shall
apply to facilities at which the potential emissions of volatile organic
compounds from all surface coating of miscellaneous parts and products equal or
exceed 10 tons per year and are located in Barrow, Bartow, Carroll, Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Hall, Henry, Newton, Paulding, Rockdale, Spalding, and Walton Counties as
follows:
| (i) |
All applicable facilities shall
comply with the provisions of subparagraphs 2., 3., 4., 5., 6., 7., and
8. |
| (ii) |
Any physical or operational
changes that are necessary to comply with the provisions specified in
subparagraphs 2., 3., or 4. are subject to the compliance schedule specified in
subparagraph 14. |
|
| 12. |
Applicability. On and after January 1, 2015, the requirements of this
subparagraph (ii) shall apply to facilities at which the potential emissions of
volatile organic compounds from all surface coating of miscellaneous parts and
products equal or exceed 100 tons per year and are located outside the counties
of Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale
Spalding, and Walton as follows:
| (i) |
All
applicable facilities shall comply with the provisions of subparagraphs 1., 5.,
6., 7., and 8. |
|
| 13. |
Applicability: The requirements of subparagraphs 11. and 12. will no longer be
applicable by the compliance deadlines if the counties specified in those
subparagraphs are re-designated to attainment for the 1997 National Ambient Air
Quality Standard for ozone prior to January 1, 2015 and such counties continue
to maintain that Standard thereafter. Instead, the provisions of subparagraphs
9. and 10. will continue to apply on and after January 1, 2015. In the event
the 1997 National Ambient Air Quality Standard for ozone is violated in the
specified counties, the requirements of subparagraphs 11. and 12. will only be
reinstated if the Director determines that the measure is necessary to meet the
requirements of the contingency plan. |
| 14. |
Compliance Schedule:
| (i) |
An application for a permit to construct
and operate volatile organic compound emission control systems and/or
modifications of process and/or coatings used must be submitted to the Division
no later than July 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed by
November 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements specified in subparagraphs 2., 3., and 4. must be completed before
January 1, 2015. |
|
|
| (jj) |
VOC Emissions from Surface Coating
of Flat Wood Paneling.
| 1. |
No person
shall cause, let, permit, suffer, or allow the emissions of VOC from surface
coating of flat wood paneling to exceed:
| (i) |
6.0 pounds per 1000 square feet of coated finished product from printed
interior panels, regardless of the number of coats applied; |
| (ii) |
12.0 pounds per 1000 square feet of
coated finished product from natural finish hardwood plywood panels, regardless
of the number of coats applied; and |
| (iii) |
10.0 pounds per 1000 square feet of
coated finished product from Class II finishes on hardboard panels, regardless
of the number of coats applied. |
|
| 2. |
The emission limits in this subparagraph
shall be achieved by:
| (i) |
the application of
low solvent coating technology where the 24-hour of all coatings on a single
coating line or operation meets the limits stated in subparagraph 1. of this
subparagraph; averaging across lines is not allowed; or |
| (ii) |
control equipment, including but not
limited to incineration, carbon adsorption and condensation, with a capture
system approved by the Director, provided that 90 percent of the nonmethane
volatile organic compounds which enter the control equipment are recovered or
destroyed, and that overall VOC emissions do not exceed the limits stated in
subparagraph 1. of this subparagraph. |
| (iii) |
control equipment demonstrated to have
control efficiency equivalent to or greater or VOC emissions equal to or less
than required in (i) or (ii) of this subparagraph and approved by the
Director. |
|
| 3. |
No person
shall cause, let, permit, suffer, or allow the emissions of VOC from the inks,
coatings, and adhesives used by flat wood paneling coating facilities to
exceed:
| (i) |
2.1 lbs VOC per gallon (250 grams
per liter) of coating, excluding water, and exempt compounds, or |
| (ii) |
2.9 lbs VOC per gallon (350 grams per
liter) of solids. |
|
| 4. |
Averaging across lines for the VOC limits in subparagraph 3. is not
permitted. |
| 5. |
Should product
performance requirements or other needs dictate the use of higher VOC coatings,
than those specified in subparagraph 3., add-on control equipment with an
overall control efficiency of 90% may be used as an alternative. |
| 6. |
Each owner or operator of a facility that
manufactures flat wood paneling shall comply with the following work practice
standards:
| (i) |
store all VOC-containing
materials in closed containers; |
| (ii) |
ensure that mixing and storage
containers used for VOC-containing materials are kept closed at all times
except when depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
materials; and |
| (iv) |
convey
VOC-containing materials from one location to another in closed containers or
pipes. |
|
| 7. |
For the purpose
of this subparagraph, the following definitions also apply:
| (i) |
"Class II hardboard paneling finish"
means finishes which meet the specifications of Voluntary Product Standard
PS-59-73 as approved by the American National Standards Institute. |
| (ii) |
"Coating application system" means all
operations and equipment which apply, convey, and dry a surface coating,
including, but not limited to, spray booths, flow coaters, conveyers, flashoff
areas, air dryers and ovens. |
| (iii) |
"Flat wood paneling" means both interior and exterior panels used in
construction and typically include decorative interior panels, exterior siding
and tileboard. Flat wood paneling includes hardboard, hardwood plywood, natural
finish hardwood plywood panels, printed interior panels, thin particleboard and
tileboard. |
| (iv) |
"Hardboard" is a
panel manufactured primarily from interfelted lignocellulosic fibers which are
consolidated under heat and pressure in a hot press. |
| (v) |
"Hardwood plywood" is plywood whose
surface layer is a veneer. |
| (vi) |
"Natural finish hardwood plywood panels" means panels whose original grain
pattern is enhanced by essentially transparent finishes frequently supplemented
by fillers and toners. |
| (vii) |
"Thin
particleboard" is a manufactured board 1/4 inch or less in thickness made of
individual wood particles which have been coated with a binder and formed into
flat sheets by pressure. |
| (viii) |
"Tileboard" means paneling that has a colored waterproof surface
coating. |
| (ix) |
"Printed interior
panels" means panels whose grain or natural surface is obscured by fillers and
basecoats upon which a simulated grain or decorative pattern is
printed. |
|
| 8. |
Applicability. Prior to January 1, 2015, the requirements of this subparagraph
(jj) shall apply to facilities at which the actual emissions of volatile
organic compounds from the surface coating of flat wood paneling equal or
exceed 15 pounds per day and are located in Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and
Rockdale Counties as follows:
| (i) |
All
applicable facilities shall comply with the provisions of subparagraphs 1., 2.,
and 7. |
|
| 9. |
Applicability.
Prior to January 1, 2015, the requirements of this subparagraph (jj) shall
apply to facilities at which the potential emissions of volatile organic
compounds from the surface coating of flat wood paneling equal or exceed 100
tons per year and are located outside the counties of Cherokee, Clayton, Cobb,
Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding,
and Rockdale Counties as follows:
| (i) |
All
applicable facilities shall comply with the provisions of subparagraphs 1., 2.,
and 7. |
|
| 10. |
Applicability.
On and after January 1, 2015, the requirements of this subparagraph (jj) shall
apply to facilities at which actual emissions of volatile organic compounds
from the surface coating of flat wood paneling, before controls, equal or
exceed 15 pounds per day (or 2.7 tons per 12-month rolling period) for
facilities located in Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton,
Paulding, Rockdale, Spalding, and Walton Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 3., 4., 5., 6., and 7. |
| (ii) |
Any physical or operational changes that
are necessary to comply with the provisions specified in subparagraphs 3., 4.,
5., or 6. are subject to the compliance schedule specified in subparagraph
13. |
|
| 11. |
Applicability. On
and after January 1, 2015, the requirements of this subparagraph (jj) shall
apply to facilities at which potential emissions of volatile organic compounds
from the surface coating of flat wood paneling equal or exceed 100 tons per
year and are located outside of counties of Barrow, Bartow, Carroll, Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Hall, Henry, Newton, Paulding, Rockdale, Spalding, and Walton Counties as
follows:
| (i) |
All applicable facilities shall
comply with the provisions of subparagraphs 1., 2., and 7. |
|
| 12. |
Applicability. The requirements of
subparagraphs 10. and 11. will no longer be applicable by the compliance
deadlines if the counties specified in those subparagraphs are re-designated to
attainment for the 1997 National Ambient Air Quality Standard for ozone prior
to January 1, 2015 and such counties continue to maintain that Standard
thereafter. Instead, the provisions of subparagraphs 8. and 9. will continue to
apply on and after January 1, 2015. In the event the 1997 National Ambient Air
Quality Standard for ozone is violated in the specified counties, the
requirements of subparagraphs 10. and 11. will only be reinstated if the
Director determines that the measure is necessary to meet the requirements of
the contingency plan. |
| 13. |
Compliance Schedule:
| (i) |
An application for a
permit to construct and operate volatile organic compound emission control
systems and/or modifications of process and/or coatings used must be submitted
to the Division no later than July 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed by
November 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements specified in subparagraph 10.(i) must be completed before
January 1, 2015. |
|
|
| (kk) |
VOC Emissions from Synthesized
Pharmaceutical Manufacturing.
| 1. |
The
owner or operator of a synthesized pharmaceutical manufacturing facility shall:
| (i) |
Control the volatile organic compound
emissions from all reactors, distillation operations, crystallizers,
centrifuges and vacuum dryers that emit 15 pounds per day or more of VOC.
Surface condensers or equivalent controls shall be used, provided that:
| (I) |
If surface condensers are used, the
condenser outlet gas temperature must not exceed:
| I. |
-13°F when condensing VOC of vapor
pressure greater than 5.8 psi, measured at 68°F; |
| II. |
5°F when condensing VOC of vapor
pressure greater than 2.9 psi, measured at 68°F; |
| III. |
32°F when condensing VOC of vapor
pressure greater than 1.5 psi, measured at 68°F; |
| IV. |
50°F when condensing VOC of vapor
pressure greater than 1.0 psi, measured at 68°F; |
| V. |
77°F when condensing VOC of vapor
pressure greater than 0.5 psi, measured at 68°F. |
|
| (II) |
If equivalent controls are used, the VOC
emissions must be reduced by at least as much as they would be by using a
surface condenser which meets the requirements of Part I. of this
subparagraph. |
|
| (ii) |
The
owner or operator of a synthesized pharmaceutical manufacturing facility
subject to this regulation shall reduce the VOC emissions from all air dryers
and production equipment exhaust systems;
| (I) |
By at least 90 percent if emissions are 330 pounds per day or more of VOC;
or |
| (II) |
33 pounds per day or less
if emissions are less than 330 pounds; |
| (III) |
The owner or operator of a synthesized
pharmaceutical manufacturing facility subject to this regulation shall:
| I. |
Provide a vapor balance system or
equivalent control that is at least 90.0 percent effective in reducing
emissions from truck or railcar deliveries to storage tanks with capacities
greater than 2,000 gallons that store VOC with vapor pressures greater than 4.1
psi at 68°F; and |
| II. |
Install
pressure/vacuum conservative vents set on all storage tanks that store VOC with
vapor pressure greater than 1.5 psi at 68°F unless a more effective control
system is used. |
|
|
| (iii) |
The owner or operator of a synthesized
pharmaceutical facility subject to this regulation shall enclose all
centrifuges, rotary vacuum filters, and other filters having an exposed liquid
surface, where the liquid contains VOC and exerts a total VOC vapor pressure of
0.5 psi or more at 68°F. |
| (iv) |
The owner or operator of a synthesized pharmaceutical facility subject to this
regulation shall install covers on all in-process tanks containing a volatile
organic compound at any time. These covers must remain closed, unless
production, sampling, maintenance, or inspection procedures require operator
access. |
| (v) |
The owner or operator
of a synthesized pharmaceutical manufacturing facility subject to this
regulation shall repair all leaks from which liquid, containing VOC, can be
observed running or dripping. The repair shall be completed the first time the
equipment is off-line for a period of time long enough to complete the
repair. |
|
| 2. |
For the
purpose of this regulation, the following definitions also apply:
| (i) |
"Condenser" means a device which cools a
gas stream to a temperature which removes specific organic compounds by
condensation; |
| (ii) |
"Control system"
means any number of control devices, including condensers, which are designed
and operated to reduce the quantity of VOC emitted to the atmosphere; |
| (iii) |
"Reactor" means a vat or vessel, which
may be jacketed to permit temperature control, designed to contain chemical
reactions; |
| (iv) |
"Separation
operation" means a process that separates a mixture of compounds and solvents
into two or more components. Specific mechanisms include extraction,
centrifugation, filtration, and crystallization; |
| (v) |
"Synthesized pharmaceutical
manufacturing" means manufacture of pharmaceutical products by chemical
synthesis; |
| (vi) |
"Production
equipment exhaust system" means a device for collecting and directing out of
the work area VOC fugitive emissions from reactor openings, centrifuge
openings, and other vessel openings for the purpose of protecting workers from
excessive VOC exposure. |
|
|
| (ll) |
VOC Emissions from the Manufacture
of Pneumatic Rubber Tires.
| 1. |
The
owner or operator of an undertread cementing, tread end cementing, or bead
dipping operation subject to this regulation shall:
| (i) |
Install and operate a capture system,
designed to achieve maximum reasonable capture from all undertread cementing,
tread and cementing and bead dipping operation; and install and operate a
control device that effects at least a 90.0 percent reduction efficiency,
measured across the control system, and has been approved by the
Director. |
| (ii) |
The owner or
operator of an undertread cementing operation, tread end cementing operation or
bead dipping operation may, in lieu of a vapor capture and control system for
those operations, make process changes which reduces emissions to a level equal
to or below that which would be achieved with emission controls as specified in
subparagraph (i) above. |
|
| 2. |
The owner or operator of a green tire
spraying operation subject to this regulation shall:
| (i) |
Substitute water-based sprays for the
normal solvent-based mold release compound; or |
| (ii) |
Comply with paragraph 1. of this
regulation. |
|
| 3. |
If the
total volatile organic compound emissions from all undertreading cementing,
tread end cementing, bead dipping and green tire spraying operations at a
pneumatic rubber tire manufacturing facility do not exceed 57 grams per tire,
paragraphs 1. and 2. above shall not apply. |
| 4. |
For the purpose of this subsection the
following definitions also apply:
| (i) |
"Pneumatic rubber tire manufacture" means the undertread cementing, tread end
cementing, bead dipping, and green tire spraying associated with the production
of pneumatic rubber, passenger type tires on a mass production basis. |
| (ii) |
"Passenger type tire" means
agricultural, airplane, industrial, mobile home, light and medium duty truck,
and passenger vehicle tires with a bead diameter up to but excluding 20.0
inches and cross section dimension up to 12.8 inches. |
| (iii) |
"Undertread cementing" means the
application of a solvent based cement to the underside of a tire
tread. |
| (iv) |
"Bead dipping" means
the dipping of an assembled tire bead into a solvent based cement. |
| (v) |
"Tread end cementing" means the
application of a solvent based cement to the tire tread ends. |
| (vi) |
"Green tires" means assembled tires
before molding and curing have occurred. |
| (vii) |
"Green tire spraying" means the
spraying of green tires, both inside and outside, with release compounds which
help remove air from the tire during molding and prevent the tire from sticking
to the mold after curing. |
| (viii) |
"Water based spray" means release compounds, sprayed on the inside and outside
of green tires, in which solids, water, and emulsifiers have been substituted
for organic solvents. |
|
|
| (mm) |
VOC Emissions from Graphic Arts
Systems.
| 1. |
No person shall cause,
let, permit, suffer, or allow the operation of a packaging rotogravure,
publication rotogravure or flexographic printing facility unless:
| (i) |
For packaging rotogravure and
flexographic printing, the VOC content of any ink or coating as applied is
equal to or less than one of the following:
| (I) |
25 percent by volume of the volatile
content of the coating or ink; or |
| (II) |
40 percent by volume of the coating or
ink, minus water; or |
| (III) |
0.5
pounds of VOC per pound of coating solids. |
|
| (ii) |
For publication rotogravure printing,
the VOC content of any ink or coating as applied is equal to or less than one
of the following:
| (I) |
25 percent by volume of
the volatile content of the coating or ink; or |
| (II) |
40 percent by volume of the coating or
ink, minus water. |
|
|
| 2. |
As an alternative to compliance with the
limits in subparagraph 1., an owner or operator of a packaging rotogravure,
publication rotogravure or flexographic printing facility may comply with the
requirements of this subparagraph by:
| (i) |
Averaging on a 24-hour weighted basis the VOC content of all inks and coatings,
as applied, on a single printing line, where the average does not exceed the
limits in subparagraph 1.; averaging across lines is not allowed; or |
| (ii) |
Installing and operating volatile
organic compound emission reduction equipment having at least 90.0 percent
reduction efficiency, and a capture system approved by the Director. |
|
| 3. |
If, as an alternative to
compliance with the limits in subparagraph 1.(i), volatile organic compound
emission reduction equipment is installed and operated at a flexible packaging
printing facility to comply with subparagraph 2.(ii) it shall have an overall
VOC control efficiency that is equal to or greater than the percentage
specified in the following subparagraphs (i) through (iv).
| (i) |
65 percent for a press that was first
installed prior to March 14, 1995, and that is controlled by an add-on air
pollution control device whose first installation date was prior to February
19, 2012; |
| (ii) |
70 percent for a
press that was first installed prior to March 14, 1995, and that is controlled
by an add-on air pollution control device whose first installation date was on
or after February 19, 2012; |
| (iii) |
75 percent for a press that was first installed on or after to March 14, 1995,
and that is controlled by an add-on air pollution control device whose first
installation date was prior to February 19, 2012; and |
| (iv) |
80 percent for a press that was first
installed on or after March 14, 1995, and that is controlled by an add-on air
pollution control device whose first installation date was on or after February
19, 2012. |
|
| 4. |
Each owner
or operator of a facility that prints flexible packaging shall comply with the
following housekeeping requirements for any affected cleaning operation:
| (i) |
store all VOC-containing cleaning
materials and used shop towels in closed containers; |
| (ii) |
ensure that storage containers used for
VOC-containing cleaning materials are kept closed at all times except when
depositing or removing these materials; |
| (iii) |
minimize spills of VOC-containing
cleaning materials; |
| (iv) |
convey
VOC-containing cleaning materials from one location to another in closed
containers or pipes; and |
| (v) |
minimize VOC emissions from cleaning of application, storage, mixing, and
conveying equipment by ensuring that equipment cleaning is performed without
atomizing the cleaning solvent and all spent solvent is captured in closed
containers. |
|
| 5. |
For the
purpose of this subparagraph, the following definitions shall apply:
| (i) |
"Cleaning" for flexible packaging
printing means cleaning of a press, press parts, or removing dried ink from
areas around a press. It does not include cleaning electronic components of a
press, cleaning in-press or post-press operations or the use of janitorial
supplies to clean areas around a press. |
| (ii) |
"Flexible packaging printing" refers to
printing upon any package or part of a package the shape of which can be
readily changed. Flexible packaging includes, but is not limited to, bags,
pouches, liners, and wraps utilizing paper, plastic, film, aluminum foil,
metalized or coated paper or film, or any combination of these
materials. |
| (iii) |
"Flexographic
printing" means the application of words, designs and pictures to a substrate
by means of a roll printing technique in which the pattern to be applied is
raised above the printing roll and the image carrier is made of rubber or other
elastomeric materials. |
| (iv) |
"Packaging rotogravure printing" means rotogravure printing upon paper,
paperboard, metal foil, plastic film, and other substrates, which are in
subsequent operations, formed into packaging products and labels for articles
to be sold. |
| (v) |
"Publication
rotogravure printing" means rotogravure printing upon paper which is
subsequently formed into books, magazines, catalogues, brochures, directories,
newspaper supplements, and other types of printed materials. |
| (vi) |
"Rotogravure printing" means the
application of words, designs and pictures to a substrate by means of a roll
printing technique which involves intaglio or recessed image areas in the form
of cells. |
| (vii) |
"Roll printing"
means the application of words, designs and pictures to a substrate usually by
means of a series of hard rubber or steel rolls each with only partial
coverage. |
|
| 6. |
Applicability. Prior to January 1, 2015, the requirements of this subparagraph
(mm) shall apply to facilities at which the potential emissions of volatile
organic compounds from packaging rotogravure, publication rotogravure, and
flexographic printing equal or exceed 25 tons per year and are located in
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2., and 5. |
|
| 7. |
Applicability. Prior to January 1, 2015,
the requirements of this subparagraph (mm) shall apply to facilities at which
the potential emissions of volatile organic compounds from packaging
rotogravure, publication rotogravure, and flexographic printing equal or exceed
100 tons per year and are located outside the counties of Cherokee, Clayton,
Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry,
Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1., 2., and 5. |
|
| 8. |
Applicability. On and after January 1,
2015, the requirements of this subparagraph (mm) shall apply to facilities at
which actual emissions of volatile organic compounds from flexible package
printing, before controls, equal or exceed 15 pounds per day (or 2.7 tons per
12-month rolling period) for facilities located in Barrow, Bartow, Carroll,
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Hall, Henry, Newton, Paulding, Rockdale, Spalding, and Walton
Counties as follows:
| (i) |
Individual presses
that have potential emissions of volatile organic compounds from flexible
package printing that equal or exceed 25 tons per year shall comply with the
provisions of subparagraphs 1.(i), 2., and 3. |
| (ii) |
Individual presses that have potential
emissions of volatile organic compounds from flexible package printing that do
not equal or exceed 25 tons per year shall comply with the provisions of
subparagraphs 1.(i) and 2. |
| (iii) |
All applicable facilities shall comply with the provisions of subparagraphs 4.,
5., and 14. |
| (iv) |
Any physical or
operational changes that are necessary to comply with the provisions specified
in subparagraph 8.(i) or (iii) are subject to the compliance schedule specified
in subparagraph 13. |
|
| 9. |
Applicability, On and after January 1, 2015, the requirements of this
subparagraph (mm) shall apply to facilities at which potential emissions of
volatile organic compounds from packaging rotogravure, publication rotogravure,
and flexographic printing equals or exceeds 25 tons per year but at which the
actual emissions of volatile organic compounds from flexible package printing,
before controls, is less than 15 pounds per day (or 2.7 tons per 12-month
rolling period) and are located in Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale
Counties as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 1., 2., and
5. |
|
| 10. |
Applicability. On
and after January 1 2015, the requirements of this subparagraph (mm) shall
apply to facilities at which potential emissions of volatile organic compounds
from packaging rotogravure, publication rotogravure, and flexographic printing
equal or exceeds 100 tons per year but at which the actual emissions of
volatile organic compounds from flexible package printing, before controls, is
less than 15 pounds per day (or 2.7 tons per 12-month rolling period) and are
located Barrow, Bartow, Carroll, Hall, Newton, Spalding, and Walton Counties as
follows:
| (i) |
All applicable facilities shall
comply with the provisions of subparagraphs 1., 2., and 5. |
|
| 11. |
Applicability. On and after January 1,
2015, the requirements of this subparagraph (mm) shall apply to facilities at
which the potential emissions of volatile organic compounds from packaging
rotogravure, publication rotogravure, and flexible package printing equal or
exceed 100 tons per year and are located outside of counties of Barrow, Bartow,
Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale, Spalding, and Walton
Counties as follows:
| (i) |
All applicable
facilities shall comply with the provisions of subparagraphs 1., 2., and
5. |
|
| 12. |
Applicability: The
requirements of subparagraphs 8., 9.,, 10., and 11. will no longer be
applicable by the compliance deadlines if the counties specified in those
subparagraphs are re-designated to attainment for the 1997 National Ambient Air
Quality Standard for ozone prior to January 1, 2015 and such counties continue
to maintain that Standard thereafter. Instead, the provisions of subparagraphs
6. and 7. will continue to apply on and after January 1, 2015. In the event the
1997 National Ambient Air Quality Standard for ozone is violated in the
specified counties, the requirements of subparagraphs 8., 9., 10., and 11. will
only be reinstated if the Director determines that the measure is necessary to
meet the requirements of the contingency plan. |
| 13. |
Compliance schedule:
| (i) |
An application for a permit to construct
and operate volatile organic compound emission control systems and/or
modifications of process and/or coatings used must be submitted to the Division
no later than July 1, 2014. |
| (ii) |
On-site of construction of emission control systems and/or modification of
process or coatings must be completed by November 1,
2014. |
| (iii) |
Full
compliance with the applicable requirements specified in subparagraph 8.(i) and
(iii) must be completed before January 1, 2015. |
|
| 14. |
Compliance determinations for
inks shall treat volatile compounds not defined as VOCs as water for the
purposes of calculating the "percent-by-volume-or-more of water" and the "less
water" parts of the ink composition. |
|
| (nn) |
VOC Emissions from External
Floating Roof Tanks.
| 1. |
No person shall
cause, let, permit, suffer, or allow the storage of petroleum liquids in
external floating roof tanks having capacities greater than 40,000 gallons
unless:
| (i) |
The vessel has been fitted with:
| (I) |
A continuous secondary seal extending
from the floating roof to the tank wall (rim-mounted secondary seal);
or |
| (II) |
A closure or other device
which controls VOC emissions with an effectiveness equal to or greater than a
seal required under Part (I) of this subparagraph and approved by the
Director. |
|
| (ii) |
All seal
closure devices meet the following requirements:
| (I) |
There are no visible holes, tears, or
other openings in the seal(s) or seal fabric; |
| (II) |
The seal(s) are intact and uniformly in
place around the circumference of the floating roof between the floating roof
and the tank wall; and |
| (III) |
For
vapor mounted primary seals, the accumulated area of gaps exceeding 1/8 inch in
width between the secondary seal and the tank wall shall not exceed 1.0 inch2
per foot of tank diameter. |
|
| (iii) |
All openings in the external floating
roof, except for automatic bleeder vents, rim space vents, and leg sleeves are:
| (I) |
Equipped with covers, seals, or lids in
the closed position except when the openings are in actual use; and |
| (II) |
Equipped with projections into the tank
which remain below the liquid surface at all times. |
|
| (iv) |
Automatic bleeder vents are closed at
all times except when the roof is floated off or landed on the roof leg
supports; |
| (v) |
Rim vents are set to
open when the roof is being floated off leg supports or at the manufacturer's
recommended setting; and |
| (vi) |
Emergency roof drains are provided with slotted membrane fabric covers or
equivalent covers which cover at least 90 percent of the area of the
opening. |
|
| 2. |
The owner or
operator of a petroleum liquid storage vessel with an external floating roof
subject to this regulation shall:
| (i) |
Perform
routine inspections semi-annually in order to insure compliance with paragraph
1. of this subsection and the inspections shall include a visual inspection of
the secondary seal gap; |
| (ii) |
Measure the secondary seal gap annually when the floating roof is equipped with
a vapor-mounted primary seal; and |
| (iii) |
Maintain records of the types of
volatile petroleum liquids stored, the maximum true vapor pressure of the
liquid as stored, and the results of the inspections performed in subparagraphs
2.(i) and (ii). |
|
| 3. |
Copies
of all records under paragraphs 2. of this subsection shall be retained by the
owner or operator for a minimum of two years after the date on which the record
was made. |
| 4. |
Copies of all records
under this section shall immediately be made available to the Director, upon
verbal or written request, at any reasonable time. |
| 5. |
The Director may, upon written notice,
require more frequent inspections or modify the monitoring and record keeping
requirements, when necessary to accomplish the purposes of this
regulation. |
| 6. |
This regulation does
not apply to petroleum liquid storage vessels which:
| (i) |
Are used to store waxy, heavy pour crude
oil; |
| (ii) |
Have capacities less than
420,000 gallons and are used to store produced crude oil and condensate prior
to lease custody transfer; |
| (iii) |
Contain a petroleum liquid with a true vapor pressure of less than 1.5
psia; |
| (iv) |
Contain a petroleum
liquid with a true vapor pressure of less than 4.0 psia; and
| (I) |
Are of welded construction; and |
| (II) |
Presently possess a metallic-type shoe
seal, a liquid mounted foam seal, a liquid-mounted liquid filled type seal, or
other closure device of demonstrated equivalence approved by the Director;
or |
| (III) |
Are of welded
construction, equipped with a metallic-type shoe primary seal and has a
secondary seal from the top of the shoe to the tank wall (shoe-mounted
secondary seal). |
|
|
| 7. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Condensate" means hydrocarbon liquid separated from natural gas which
condenses due to changes in the temperature and/or pressure and remains liquid
at standard conditions. |
| (ii) |
"Crude
oil" means a naturally occurring mixture which consists of hydrocarbons and
sulfur, nitrogen and/or oxygen derivatives of hydrocarbons which is a liquid at
standard conditions. |
| (iii) |
"Lease
custody transfer" means the transfer of produced crude oil and/or condensate,
after processing and/or treating in the producing operations, from storage
tanks or automatic transfer facilities to pipelines or any other forms of
transportation. |
| (iv) |
"External
floating roof" means a storage vessel cover in an open top tank consisting of a
double deck or pontoon single deck which rests upon and is supported by the
petroleum liquid being contained and is equipped with a closure seal or seals
to close the space between the roof edge and tank wall. |
| (v) |
"Liquid-mounted seal" means a primary
seal mounted in continuous contact with the liquid between the tank wall and
the floating roof around the circumference of the tank. |
| (vi) |
"Petroleum liquids" means crude oil,
condensate, and any finished or intermediate products manufactured or extracted
in a petroleum refinery. |
| (vii) |
"Vapor-mounted seal" means a primary seal mounted so there is an annular vapor
space underneath the seal. The annular vapor space is bounded by the bottom of
the primary seal, the tank wall, the liquid surface and the floating
roof. |
| (viii) |
"Waxy, heavy pour
crude oil" means a crude oil with a pour point of 50°F or higher as
determined by the American Society for Testing and Materials Standards D97-66,
"Test for Pour Point of Petroleum Oils." |
|
|
| (oo) |
Fiberglass Insulation
Manufacturing Plants.
| 1. |
No person
shall cause, let, suffer, permit or allow the emission of particulate matter
from any fiberglass insulation production line to exceed a concentration of
0.04 grains per standard dry cubic foot. |
| 2. |
For the purpose of this subsection,
"Fiberglass insulation production line" means any combination of equipment,
devices or contrivances for the manufacture of fiberglass insulation. This does
not include glass melting furnaces, equipment associated with the process which
is defined herein as "Fuel-burning Equipment," equipment the primary purpose of
which involves the handling, storing or packaging of the fiberglass insulation
or equipment the primary purpose of which involves the handling, storing or
conveying of raw products for input into the glass melting furnace. |
|
| (pp) |
Bulk Gasoline
Plants.
| 1. |
After the compliance date
specified in paragraph 6. of this subsection, no owner or operator of a bulk
gasoline plant may permit the receiving or dispensing of gasoline by its
stationary storage tanks unless:
| (i) |
Each
stationary storage tank is equipped with a submerged fill pipe, approved by the
Director; or |
| (ii) |
Each stationary
storage tank is equipped with a fill line whose discharge opening is at the
tank bottom. |
| (iii) |
Each stationary
storage tank has a vapor balance system consisting of the following major
components:
| (I) |
A vapor space connection on
the stationary storage tank equipped with fittings which are vapor tight and
will automatically and immediately close upon disconnection so as to prevent
release of gasoline or gasoline vapors; and |
| (II) |
A connecting pipe or hose equipped with
fittings which are vapor tight and will automatically and immediately close
upon disconnection so as to prevent release of gasoline or gasoline
vapors. |
|
|
| 2. |
After the compliance date specified in paragraph 6. of this subsection, no
owner or operator of a bulk gasoline plant, or the owner or operator of a tank
truck or trailer may permit the transfer of gasoline between the tank truck or
trailer and stationary storage tank unless:
| (i) |
The vapor balance system is in good
working order and is connected and operating; |
| (ii) |
The gasoline transport vehicle is
maintained to prevent the escape of fugitive vapors and gasses during loading
operations; |
| (iii) |
A means is
provided to prevent liquid drainage from the loading device when it is not in
use or to accomplish complete drainage before the loading device is
disconnected; and |
| (iv) |
The pressure
relief valves on storage vessels and tank trucks or trailers are set to release
at 0.7 psia or greater unless restricted by state or local fire codes or the
National Fire Prevention Association guidelines in which case the pressure
relief valve must be set to release at the highest possible pressure allowed by
these codes or guidelines. |
|
| 3. |
The requirements of this subsection shall
not apply to stationary storage tanks of less than 2,000 gallons. |
| 4. |
Sources and persons affected under this
subsection shall comply with the vapor collection and control system
requirements of subsection 391-3-1-.02(2)(ss). |
| 5. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Bottom
filling" means the filling of a tank truck or stationary storage tank through
an opening that is located at the tank bottom. |
| (ii) |
"Bulk gasoline plant" means a gasoline
storage and distribution facility with an average daily throughput of more than
4,000 gallons but less than 20,000 gallons which receives gasoline from bulk
terminals by rail and/or trailer transport, stores it in tanks, and
subsequently dispenses it via account trucks to local farms, businesses, and
service stations. |
| (iii) |
"Bulk
gasoline terminal" means a gasoline storage facility which receives gasoline
from refineries primarily by pipeline, ship, or barge, and delivers gasoline to
bulk gasoline plants or to commercial or retail accounts primarily by tank
truck and has an average daily throughput of more than 20,000 gallons of
gasoline. |
| (iv) |
"Gasoline" means any
petroleum distillate having a Reid vapor pressure of 4.0 psia or
greater. |
| (v) |
"Stationary Storage
Tank" means all underground vessels and any aboveground vessels never intended
for mobile use. |
| (vi) |
"Submerged
filling," means the filling of a tank truck or stationary tank through a pipe
or hose whose discharge opening is not more than six inches from the tank
bottom. |
| (vii) |
"Vapor balance
system" means a combination of pipes or hoses that create a closed system
between the vapor spaces of an unloading tank and a receiving tank such that
vapors displaced from the receiving tank are transferred to the tank being
unloaded. |
|
| 6. |
Compliance
Dates.
| (i) |
All bulk gasoline plants located in
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale counties shall be in
compliance. |
| (ii) |
All bulk gasoline
plants located in Catoosa, Richmond and Walker counties shall be in compliance
with this subsection by May 1, 2006. |
| (iii) |
All bulk gasoline plants located in
Barrow, Bartow, Carroll, Hall, Newton, Spalding, and Walton counties shall be
in compliance with this subsection by June 1, 2008. |
|
|
| (qq) |
VOC Emissions from
Large Petroleum Dry Cleaners.
| 1. |
No
person shall cause, let, permit, suffer or allow the emissions of VOC from a
large petroleum dry cleaner facility to exceed 3.5 pounds per 100 pounds dry
weight of articles dry cleaned. |
| 2. |
The VOC content in all filtration waste shall be reduced to one pound or less
per hundred pounds dry weight of articles dry cleaned before disposal and
exposure to the atmosphere from a petroleum solvent filtration system;
or |
| 3. |
Install and operate a
cartridge filtration system and drain the filter cartridges in the sealed
housing for eight hours or more before their removal. |
| 4. |
Each owner or operator of a large
petroleum dry cleaner shall inspect all equipment for leaks every 15 days and
repair all petroleum solvent vapor and liquid leaks within three working days
after identifying the source of the leaks. |
| 5. |
Each owner or operator of a large
petroleum dry cleaner shall maintain sufficient records to demonstrate
compliance and provide them to the Division upon request, for a period of two
years. |
| 6. |
For the purpose of this
subsection, the following definitions shall apply:
| (i) |
"Cartridge filter" means perforated
canisters containing filtration paper and activated carbon that are used in the
pressurized system to remove solid particles and fugitive dyes from soil-laden
solvents. |
| (ii) |
"Large petroleum dry
cleaner" means any facility engaged in the process of the cleaning of textile
and fabric products in which articles are washed in a nonaqua solution
(solvent), then dried by exposure to a heated air stream and consumes 25 tons
or more of a petroleum solvent annually. |
| (iii) |
"Solvent recovery dryer" means a class
of dry cleaning dryers that employs a condenser to liquefy and recover solvent
vapors evaporated in a closed loop recirculating stream of heated
air. |
|
|
| (rr) |
Gasoline Dispensing Facility - Stage I.
| 1. |
Requirements: After the compliance date
specified in subparagraph 16 of this subparagraph, no person may transfer or
cause or allow the transfer of gasoline from any delivery vessel into any
stationary storage tank subject to subparagraph (rr), unless:
| (i) |
The stationary storage tank is equipped
with all of the following:
| (I) |
A submerged
fill pipe; and |
| (II) |
A Division
approved Gasoline Vapor Recovery System as noted below:
| A. |
An Enhanced Stage I Gasoline Vapor
Recovery System as defined in subparagraph 15.(iv) that shall remain in good
working condition, such as keeping the vapor return opening free of liquid or
solid obstructions, and that also shall be leak tight as determined by tests
conducted in accordance with test procedures as approved by the Division;
or |
| B. |
For existing gasoline
dispensing facilities in Catoosa, Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, Richmond,
Rockdale, and Walker counties, a Stage I Gasoline Vapor Recovery System as
defined in subparagraph 15.(x) that shall remain in good working condition;
and |
|
| (III) |
Vents that
shall be at least 12 feet in height from the ground and shall have a
Pressure/Vacuum vent valve with settings as specified by applicable Stage I or
II vapor recovery CARB executive order. In systems where vents have manifolds,
the manifold may be less than 12 feet. |
|
| (ii) |
The vapors displaced from the gasoline
stationary storage tank during filling are controlled by one of the following:
| (I) |
A vapor-tight vapor return line from the
gasoline stationary storage tank(s) to the delivery vessel for each product
delivery line that is connected from the delivery vessel to the gasoline
stationary storage tank(s) and a method or procedure that will ensure the vapor
line(s) is connected before gasoline can be transferred into the gasoline
stationary storage tank(s); or |
| (II) |
If a manifold connects all gasoline stationary storage tanks vent lines, a
vapor-tight vapor return line from a gasoline stationary storage tank being
filled to the delivery vessel with sufficient return capacity to control vapors
from all gasoline stationary storage tanks being filled at the time and to
prevent release of said vapors from the vent line(s) or other gasoline
stationary storage tank openings, however, no more than two tanks shall be
filled at the same time per connected vapor-tight return line; or |
| (III) |
A refrigeration-condensation system or
a carbon adsorption system is utilized and recovers at least 90 percent by
weight of the organic compounds. |
|
|
| 2. |
Applicability: The requirements contained
in this subparagraph shall apply to all stationary storage tanks with
capacities of 2,000 gallons or more which were in place before January 1, 1979,
and stationary storage tanks with capacities of 250 gallons or more which were
in place after December 31, 1978, located at gasoline dispensing facilities
located in those counties of Barrow, Bartow, Carroll, Catoosa, Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Hall, Henry, Paulding, Richmond, Rockdale, Spalding, Newton, Walker and
Walton. |
| 3. |
Applicability: Once a
gasoline dispensing facility becomes subject to this rule, it will continue to
be subject even if the gasoline average throughput rate falls below the
applicability threshold. |
| 4. |
Exemptions: The requirements of this subparagraph shall not apply to stationary
storage tanks of less than 550 gallons capacity used exclusively for the
fueling of implements of husbandry or to gasoline dispensing facilities that
dispense no more than 10,000 gallons average monthly throughput rate of
gasoline per month, provided the tanks are equipped with submerged fill
pipes. |
| 5. |
Stage I Gasoline Vapor
Recovery Systems installed prior to January 1, 1993 that currently utilize a
co-axial Stage I vapor recovery system in which the gasoline stationary storage
tanks are not manifolded in any manner and that are utilized at a facility that
is not required to have a Stage II vapor recovery system shall be exempted from
installing a co-axial poppetted drop tube. All co-axial Stage I Gasoline Vapor
Recovery Systems must be upgraded to Enhanced Stage I Gasoline Vapor Recovery
Systems before May 1, 2012. |
| 6. |
Certification and Recertification Testing Requirements: All Stage I Gasoline
Vapor Recovery Systems and Enhanced Stage I Gasoline Vapor Recovery Systems at
gasoline dispensing facilities shall be certified by the equipment owner as
being properly installed and properly functioning in accordance with the
applicable CARB Executive Order. Certification and recertification testing
shall be conducted by a qualified technician who has a thorough knowledge of
the system. Tests shall be conducted in accordance with test procedures as
approved by the Division. The fill cap and vapor cap must be removed when
performing certification testing. |
| 7. |
Certification and Recertification Testing
Requirements: Testing may be conducted by the Division or by an installation or
testing company that meets the minimum criteria established by the Division for
conducting such tests. In the case where a party other than the Division will
be conducting the testing, the owner or operator shall notify the Division at
least five business days in advance as to when and where the testing will
occur, what party will conduct the testing, and the CARB Executive Order
number. For Enhanced Stage I Gasoline Vapor Recovery Systems, a certified and
trained individual is required to install and test the System in accordance
with the applicable CARB Executive Order. |
| 8. |
Certification and Recertification Testing
Requirements: Certification, recertification, and testing and compliance
reporting for all Stage I gasoline vapor recovery systems shall be required
according to the following schedule:
| (i) |
Certification testing is required within 30 days of system installation for
Stage I gasoline vapor recovery systems approved by the Division after December
31, 2002. |
| (ii) |
Certification
testing is required within 30 days of system installation for Enhanced Stage I
Gasoline Vapor Recovery Systems approved by the Division installed after
December 31, 2002. |
| (iii) |
After June
1, 2008, recertification testing will be required within 12 months following
the initial certification or recertification for Stage I Gasoline Vapor
Recovery Systems approved by the Division. |
| (iv) |
After June 1, 2008 recertification
testing will be required within 24 months following the initial certification
or recertification for Enhanced Stage I Gasoline Vapor Recovery Systems
approved by the Division. |
|
| 9. |
Reporting Requirements: Compliance
reporting shall be required within 30 days of the certification or
recertification test(s) required by subparagraph 8. This report shall be
submitted to the Division and shall include results of all tests conducted for
certification or recertification. |
| 10. |
Maintenance Requirements: The owner or
operator of the gasoline dispensing facility shall maintain the Enhanced Stage
I Gasoline Vapor Recovery System or Stage I Gasoline Vapor Recovery System in
proper operating condition as specified by the manufacturer and free of defects
that could impair the effectiveness of the system. For the purposes of this
subparagraph, the following is a list of equipment defects that substantially
impair the effectiveness of the systems in reducing gasoline bulk transfer and
fugitive vapor emissions:
| (i) |
Absence or
disconnection of any component that is a part of the approved system; |
| (ii) |
Pressure/vacuum relief valves or dry
breaks and drain valves in the spill bucket that are inoperative; and |
| (iii) |
Any visible product leaks. |
|
| 11. |
Maintenance Requirements: Upon
identification of any of the defects as described above, the owner or operator
of the gasoline dispensing facility shall immediately schedule and implement
repair, replacement or adjustment by the company's repair representative as
necessary. |
| 12. |
Recordkeeping
Requirements: The following records shall be maintained on-site for two years:
| (i) |
Maintenance records including any
repaired or replacement parts and a description of the problems; |
| (ii) |
Compliance records including warnings or
notices of violation issued by the Division; and |
| (iii) |
Gasoline throughput records that will
allow the average monthly gasoline throughput rate to be continuously
determined. |
|
| 13. |
Recordkeeping Requirements: Record disposal may be approved by the Division
upon a written request by the owner or operator of the gasoline dispensing
facility. Approval may be granted on a case-by-case basis considering volume of
records, number of times the records have been inspected by the Division; and
the value of maintaining the records. In no case, shall the time be extended
beyond the requirements of this subparagraph. |
| 14. |
Compliance Inspections: Gasoline
dispensing facilities equipped with Enhanced Stage I Gasoline Vapor Recovery
Systems and Stage I Gasoline Vapor Recovery Systems shall be subject to annual
compliance inspections and functional testing by the Environmental Protection
Division personnel which include but are not limited to the following:
| (i) |
Verification that all equipment is
present and maintains a certified system configuration as defined in
subparagraphs 15.(iv). or 15.(x), whichever is applicable. |
| (ii) |
Inspection of all Stage I vapor recovery
related files to ensure that the gasoline dispensing facility has complied with
maintenance requirements and other record keeping requirements such as
inspection, compliance and volume reports as required by subparagraphs 10.,
11., 12., and 13.. |
| (iii) |
Observation of the use of equipment by facility operators and product
suppliers. |
| (iv) |
Verification that
the facility has complied with the certification and/or recertification testing
requirements as specified by subparagraphs 6., 7., and 8., whichever is
applicable. |
|
| 15. |
Definitions: For the purpose of this subparagraph, the following definitions
shall apply:
| (i) |
"Average monthly throughput
rate" means the average of the gallons pumped monthly for the most recent two
year period of operation excluding any inactive period. If a facility has not
been in operation for two years or does not have access to records for the most
recent two years of operation, the Division shall determine the length of time
to determine the average of the gallons pumped monthly. |
| (ii) |
"CARB" means the California Air
Resources Board. |
| (iii) |
"Delivery
vessel" means tank trucks or trailers equipped with a storage tank and used for
the transport of gasoline from sources of supply to stationary storage tanks of
gasoline dispensing facilities. |
| (iv) |
"Enhanced Stage I Gasoline Vapor
Recovery System" means:
| (I) |
any Stage I
gasoline vapor recovery system properly certified under current version of the
CARB vapor recovery certification procedures and applicable executive order
effective on or after April 1, 2001; or |
| (II) |
any Stage I gasoline vapor recovery
system whose design has been submitted to the Division, has passed any required
certification tests, demonstrated an efficiency of 98% collection of vapors,
and whose owner/operator has received a written approval from the Division. The
submitted design shall include but may not be limited to drawings detailing all
components of the system and a written narrative describing the components and
their use. |
|
| (v) |
"Existing
gasoline dispensing facility" means any applicable gasoline dispensing facility
with an approved Stage I Gasoline Vapor Recovery System that was in operation
on or before April 30, 2008. |
| (vi) |
"Gasoline" means a petroleum distillate having a Reid vapor pressure of 4.0
psia or greater. |
| (vii) |
"Gasoline
dispensing facility" means any site where gasoline is dispensed to motor
vehicle gasoline tanks from stationary storage tanks. |
| (viii) |
"Major Modification" means the
addition, replacement, or removal of a gasoline storage tank or a modification
that causes the tank top of an underground storage tank to be
unburied. |
| (ix) |
"Reconstruction"
means the replacement of any stationary gasoline storage tank. |
| (x) |
"Stage I Gasoline Vapor Recovery System"
means:
| (I) |
any Stage I Gasoline Vapor Recovery
System properly certified under the CARB vapor recovery certification
procedures effective before April 1, 2001, excluding the coaxial poppetted drop
tube requirement exempted by subparagraph 5; or |
| (II) |
any Stage I Gasoline Vapor Recovery
System whose design has been submitted to the Division, has passed any required
certification tests, and whose owner/operator has received a written approval
from the Division. The submitted design shall include but may not be limited to
drawings detailing all components of the system and a written narrative
describing the components and their use. Mixing of equipment components
certified under separate certification procedures may be allowed when supported
by manufacturer or independent third-party certification that the configuration
meets or exceeds the applicable performance standards and has received prior
written approval from the Division. |
|
| (xi) |
"Stationary storage tank" means all
underground vessels and any aboveground vessels never intended for mobile
use. |
| (xii) |
"Submerged fill pipe"
means any fill pipe with a discharge opening which is within a nominal distance
of six inches from the tank bottom. |
|
| 16. |
Compliance Dates
| (i) |
All gasoline dispensing facilities
located in Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Henry, Paulding and Rockdale counties shall be in
compliance. |
| (ii) |
All gasoline
dispensing facilities located in Catoosa, Richmond and Walker counties that
dispense more than 50,000 gallons of gasoline per month shall be in compliance
with this subparagraph by May 1, 2006. |
| (iii) |
All gasoline dispensing facilities
located in Catoosa, Richmond and Walker counties that dispense 50,000 gallons
or less of gasoline per month shall be in compliance with this subparagraph by
May 1, 2007. |
| (iv) |
All gasoline
dispensing facilities that dispense 100,000 gallons average monthly throughput
of gasoline or more per month located in Barrow, Bartow, Carroll, Hall,
Spalding, Newton and Walton counties shall be in compliance with this
subparagraph by June 1, 2008. |
| (v) |
All gasoline dispensing facilities that dispense greater than or equal to
50,000 gallons and less than 100,000 gallons average monthly throughput of
gasoline per month located in Barrow, Bartow, Carroll, Hall, Spalding, Newton
and Walton counties shall be in compliance with this subparagraph by November
1, 2008. |
| (vi) |
All gasoline
dispensing facilities that dispense greater than 10,000 gallons and less than
50,000 gallons average monthly throughput of gasoline-per-month and are located
in Barrow, Bartow, Carroll, Hall, Spalding, Newton and Walton counties shall be
in compliance with this subparagraph by March 1, 2009. |
| (vii) |
Upon the effective date of this rule,
all newly constructed or reconstructed gasoline dispensing facilities located
in Barrow, Bartow, Carroll, Catoosa, Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Paulding, Richmond,
Rockdale, Spalding, Newton, Walker and Walton shall be in compliance with this
subparagraph upon startup of gasoline dispensing operations. |
| (viii) |
Upon the effective date of this rule,
all existing gasoline dispensing facilities located in Catoosa, Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Henry, Paulding, Richmond, Rockdale, and Walker counties that undergo major
modification shall be in compliance with the requirements of an approved
Enhanced Stage I Gasoline Vapor Recovery System as defined in subparagraph
15.(iv) upon completion of the modification. |
| (ix) |
All existing gasoline dispensing
facilities located in Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and Rockdale counties shall
be in compliance with the requirements of an approved Enhanced Stage I Gasoline
Vapor Recovery System as defined in subparagraph 15.(iv) before May 1,
2012. |
| (x) |
All existing gasoline
dispensing facilities located in Catoosa, Richmond, and Walker counties shall
be in compliance with the requirements of an approved Enhanced Stage I Gasoline
Vapor Recovery System as defined in subparagraph 15.(iv) before May 1,
2023. |
|
|
| (ss) |
Gasoline Transport Vehicles and Vapor Collection Systems.
| 1. |
After the compliance date specified in
paragraph 6. of this subparagraph, no person shall cause, let, permit, suffer,
or allow the loading or unloading of gasoline from a gasoline transport vehicle
of any size capacity unless:
| (i) |
The tank
sustains a pressure change of not more than three inches of water in five
minutes when pressurized to 18 inches of water and evacuated to six inches of
water as tested at least once per year in accordance with test procedures
specified by the Division; |
| (ii) |
Displays a marking on the right front (passenger) side of the tank, in
characters at least 2 inches high, which reads either P/V TEST DATE or EPA27
and the date on which the gasoline transport tank was last tested; |
| (iii) |
The tank has no visible liquid leaks
and no gasoline vapor leaks as measured by a combustible gas
detector; |
| (iv) |
The owner or
operator of the gasoline transport vehicle has submitted to the Division within
30 days of the test date a data sheet in the format specified by the Division
containing at a minimum the following information: name of person(s) or company
that conducted the test, date of test, test results including a list of any
repairs made to the transport vehicle to bring it into compliance and the
manufacturer's vehicle identification number (VIN) of the tank truck or frame
number of a trailer-mounted tank; and |
| (v) |
The transport vehicle has been equipped
with fittings which are vapor tight and will automatically and immediately
close upon disconnection so as to prevent release of gasoline or gasoline
vapors, with a vapor return line and hatch seal designed to prevent the escape
of gasoline or gasoline vapors while loading. |
|
| 2. |
The owner or operator of a vapor
collection and vapor control system shall:
| (i) |
Design and operate the vapor collection and vapor control system and the
gasoline loading equipment in a manner that prevents:
| (I) |
Gauge pressure from exceeding 18 inches
of water and vacuum from exceeding six inches of water in the gasoline tank
truck; |
| (II) |
A reading equal to or
greater than 100 percent of the lower explosive limit (LEL, measured as
propane) at one inch from all points on the perimeter of a potential leak
source when measured (in accordance with test procedures specified by the
Division) during loading or unloading operations at gasoline dispensing
facilities, bulk gasoline plants and bulk gasoline terminals; and |
| (III) |
Avoidable visible liquid leaks during
loading and unloading operations at gasoline dispensing facilities, bulk
gasoline plants and bulk gasoline terminals. |
|
| (ii) |
Within 15 days, repair and retest a
vapor collection or vapor control system that exceeds the limits in
Subparagraph (i) above. |
|
| 3. |
Applicability: The requirements of this
subparagraph shall apply only to those gasoline transport vehicles which load
or unload gasoline at bulk gasoline terminals, bulk gasoline plants, and
gasoline dispensing facilities subject to VOC vapor control requirements
contained under section 391-3-1-.02(2). |
| 4. |
The Division may require a pressure/vacuum
retest or leak check for any gasoline transport vehicle, vapor collection
system, vapor control system, and/or gasoline loading equipment subject to this
subparagraph. A gasoline transport vehicle, vapor collection system, vapor
control system, and/or gasoline loading equipment for which the Division has
required a pressure/vacuum retest or leak check shall:
| (i) |
Cease loading and unloading operations
within fourteen (14) days of the date of the initial retest or leak check
request unless the retest or leak check has been completed to the satisfaction
of the Division; |
| (ii) |
Provide
written advance notification to the Division of the scheduled time and place of
the test in order to provide the Division an opportunity to have an observer
present; and |
| (iii) |
Supply a copy of
the results of all such tests to the Division within 30 days of the test
date. |
|
| 5. |
For the purpose
of this subparagraph, the following definitions shall apply:
| (i) |
"Combustible Gas Detector" means a
portable VOC gas analyzer with a minimum range of 0-100 percent of the LEL as
propane. |
| (ii) |
"Gasoline" means a
petroleum distillate having a Reid vapor pressure of 4.0 psia or
greater. |
| (iii) |
"Gasoline Transport
Vehicle" means any mobile storage vessel including tank trucks and trailers
used for the transport of gasoline from sources of supply to stationary storage
tanks of gasoline dispensing facilities, bulk gasoline plants or bulk gasoline
terminals. |
| (iv) |
"Gasoline Vapor
Leak" means a reading of 100 percent or greater of the Lower Explosive Limit
(LEL) of gasoline when measured as propane at a distance of one inch. |
| (v) |
"Vapor Collection System" means a vapor
transport system, including any piping, hoses and devices, which uses direct
displacement by the gasoline being transferred to force vapors from the vessel
being loaded into either a vessel being unloaded or vapor control system or
vapor holding tank. |
| (vi) |
"Vapor
Control System" means a system, including any piping, hoses, equipment and
devices, that is designed to control the release of volatile organic compounds
displaced from a vessel during transfer of gasoline. |
|
| 6. |
Compliance Dates.
| (i) |
All gasoline transport vehicles and vapor
collection systems operating in Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and Rockdale
counties shall be in compliance. |
| (ii) |
All gasoline transport vehicles and
vapor collection systems operating in Catoosa, Richmond and Walker counties
shall be in compliance with this subparagraph by May 1, 2006. |
| (iii) |
All gasoline transport vehicles and
vapor collection systems operating in Barrow, Bartow, Carroll, Hall, Newton,
Spalding, and Walton counties shall be in compliance with this subparagraph by
June 1, 2008. |
|
|
| (tt) |
VOC Emissions from Major
Sources.
| 1. |
No person shall cause, let,
permit, suffer or allow the emissions of VOC from any source to exceed the
levels specified in paragraph 3. below unless such source has been approved by
the Director as utilizing all reasonably available control technology in
controlling those VOC emissions. |
| 2. |
For the purpose of this subsection, "Reasonably Available Control Technology"
means the utilization and/or implementation of water based or low solvent
coatings, VOC control equipment such as incineration, carbon adsorption,
refrigeration or other like means as determined by the Director to represent
reasonably available control technology for the source category in
question. |
| 3. |
The requirements
contained in this subsection shall apply to all such sources located in the
counties of Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Henry, Paulding, and Rockdale which have potential VOC
emissions exceeding 25 tons-per-year and to all such sources in the counties of
Barrow, Bartow, Carroll, Hall, Newton, Spalding, and Walton which have
potential VOC emissions exceeding 100 tons-per-year. |
| 4. |
Compliance Dates.
| (i) |
All sources of VOC emissions subject to
this subsection and located in the counties of Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and
Rockdale shall be in compliance. |
| (ii) |
All sources of VOC emissions subject to
this subsection located in the counties of Bartow, Carroll, Hall, Newton,
Spalding, and Walton and in operation on or before October 1, 1999, shall
comply with the following compliance schedule:
| (I) |
A demonstration of appropriate reasonably
available control technology for controlling VOC emissions from the source must
be submitted to the Division no later than October 1, 2000. Each demonstration
is subject to approval, denial, or modification by the Division. |
| (II) |
A final control plan and application for
a permit to construct for the installation of VOC emission control systems
and/or modification of coatings, solvents, processes, or equipment must be
submitted to the Division no later than April 1, 2001. |
| (III) |
On-site construction of emission
control systems and/or modification of coatings, solvents, processes, or
equipment must be completed by March 1, 2003. |
| (IV) |
Full compliance with the applicable
requirements of this subsection must be demonstrated through methods and
procedures approved by Division on or before May 1, 2003. |
|
| (iii) |
All sources of VOC emissions subject to
this subsection located in the counties of Bartow, Carroll, Hall, Newton,
Spalding, and Walton and which begin initial operation after October 1, 1999,
shall be in compliance upon startup. |
| (iv) |
All sources of VOC emissions subject to
this subsection and located in Barrow County shall be in compliance by March 1,
2009. |
|
| 5. |
For the purpose
of determining applicability of this subsection, the emissions of VOC from any
source shall exclude all VOC emissions subject to any other more specific VOC
requirements contained in other subsections of this Rule. |
| 6. |
For all Reasonably Available Control
Technology demonstrations approved or determined pursuant to this subsection,
the Division shall issue a public notice which provides for an opportunity for
public comment and an opportunity for a hearing on the determination. |
| 7. |
All Reasonably Available Control
Technology demonstrations, and any modifications or changes to those
determinations, approved or determined by the Division pursuant to this
subsection shall be submitted by the Division to the U.S. EPA as a revision to
the state implementation plan. No Reasonably Available Control Technology
demonstration, nor any modification or change to a demonstration, approved or
determined by the Division pursuant to this subsection shall revise the state
implementation plan or be used as a state implementation plan credit, until it
is approved by the U.S. EPA as a state implementation plan revision. |
|
| (uu) |
Visibility
Protection.
| 1. |
The Director shall
provide written notice of any permit application or written advance notice of a
permit application for a proposed major stationary source or major modification
to an existing major stationary source of emissions from which may have an
impact on visibility in a Class I area to the federal land manager and the
federal official charged with direct responsibility for management of any land
within any such area. |
| 2. |
The
Director shall provide such notice within 30 days after receiving an
application or written advance notice from a source as described in paragraph
1. above. The notification of a permit application shall include an analysis of
the proposed source's anticipated impact on visibility in any federal Class I
area and all materials in the application. In addition, the Director shall
provide the Federal Land Manager a 60-day notice of any public hearing on that
permit application. |
| 3. |
The Director
shall consider any analysis performed and/or written comments made by the
Federal Land Manager in any final determination regarding the issuance of the
permit provided that such analysis and/or comments are received within 30 days
of having been notified by the Division. Where such analysis does not
demonstrate to the satisfaction of the Director that an adverse impact will
occur, the Director shall explain his decision and give notice of where the
explanation can be obtained. |
| 4. |
The
provisions of this paragraph shall apply regardless of whether the proposed
facility is to be located in an attainment, unclassified or non-attainment
area. |
| 5. |
The Director may require
the source to monitor visibility in any Class I Federal area near the proposed
new stationary source or major modification for such purposes and by such means
as the Director deems necessary and appropriate. |
| 6. |
For the purpose of this paragraph, major
stationary source or major modification to an existing source shall be defined
as in 40 CFR 51.24, but only for the pollutants of particulate matter, sulfur
dioxide and nitrogen oxides. |
| 7. |
Prior to the issuance of any permit, the Director shall ensure that the
source's emissions will be consistent with making reasonable progress towards
the national visibility goal of preventing any future, and remedying any
existing, impairment of visibility in mandatory Class I areas which impairment
results from manmade air pollution. The Director may take into account the cost
of compliance, the time necessary for compliance, the energy and non-air
quality environmental impacts of compliance, and the useful life of the
source. |
| 8. |
For the purpose of this
paragraph, "impact on visibility" means visibility impairment (reductions in
visual range and atmospheric discoloration) which interferes with the
management, protection, preservation or enjoyment of the visitor's visual
experience of the Federal Class I area. This determination must be made on a
case-by-case basis taking into account the geographic extent, intensity,
duration, frequency and time of visibility impairment, and must have these
factors correlate with:
| (i) |
Times of visitor
use of the Federal Class I area; and |
| (ii) |
The frequency and timing of natural
conditions that reduce visibility. |
|
|
| (vv) |
Volatile Organic Liquid Handling
and Storage.
| 1. |
After the compliance
date specified in section 3. of this subsection, no person subject to other VOC
requirements contained in other subsections of this Rule may transfer or cause
or allow the transfer of any volatile organic liquid other than gasoline from
any delivery vessel into a stationary storage tank of greater than 4,000
gallons, unless the tank is equipped with submerged fill pipes. |
| 2. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Delivery Vessel" means any tank truck or trailer equipped with a storage tank
in use for the transport of volatile organic liquids from sources of supply to
stationary storage tanks; and |
| (ii) |
"Submerged Fill Pipe" means any fill pipe with a discharge opening which is
within six inches of the tank bottom. |
|
| 3. |
Compliance Dates.
| (i) |
All volatile organic liquid handling and
storage facilities located in the counties of Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and
Rockdale shall be in compliance. |
| (ii) |
All volatile organic liquid handling and
storage facilities subject to this subsection; located in the counties of
Bartow, Carroll, Hall, Newton, Spalding, and Walton; and in operation on or
before October 1, 1999, shall be in compliance by May 1, 2003. |
| (iii) |
All volatile organic liquid handling
and storage facilities subject to this subsection; located in the counties of
Bartow, Carroll, Hall, Newton, Spalding, and Walton; and which begin initial
operation after October 1, 1999, shall be in compliance upon startup. |
| (iv) |
All volatile organic liquid handling and
storage facilities subject to this subsection and located in Barrow County
shall be in compliance by March 1, 2009. |
|
|
| (yy) |
Emissions of Nitrogen Oxides from
Major Sources.
| 1. |
No person shall
cause, let, permit, suffer or allow the emissions of nitrogen oxides from any
source to exceed the levels specified in paragraph 2. below unless such source
has been approved by the Director as meeting the appropriate requirement for
all reasonably available control technology in controlling those emissions of
nitrogen oxides. |
| 2. |
The
requirements contained in this subsection shall apply to all such sources
located in the counties of Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale which have
potential emissions of nitrogen oxides, expressed as nitrogen dioxide,
exceeding 25 tons-per-year and to all such sources in the counties of Barrow,
Bartow, Carroll, Hall, Newton, Spalding, and Walton which have potential
emissions of nitrogen oxides, expressed as nitrogen dioxide, exceeding 100
tons-per-year. |
| 3. |
Compliance Dates.
| (i) |
All sources of nitrogen oxides emissions
subject to this subsection which have potential emissions of nitrogen oxides,
expressed as nitrogen dioxide, exceeding 50 tons per year; were in operation on
or before April 1, 2004; and are located in the counties of Cherokee, Clayton,
Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry,
Paulding and Rockdale shall be in compliance. |
| (ii) |
All sources of nitrogen oxides emissions
subject to this subsection located in the counties of Bartow, Carroll, Hall,
Newton, Spalding, and Walton and in operation on or before October 1, 1999,
shall comply with the following compliance schedule:
| (I) |
A demonstration of appropriate reasonably
available control technology for controlling emissions of nitrogen oxides from
the source must be submitted to the Division no later than October 1, 2000.
Each demonstration is subject to approval, denial, or modification by the
Division. |
| (II) |
A final control plan
and application for a permit to construct for the installation of nitrogen
oxides emission control systems and/or modifications of process or fuel-burning
equipment must be submitted to the Division no later than April 1,
2001. |
| (III) |
On-site construction of
emission control systems and/or modification of process or fuel-burning
equipment must be completed by March 1, 2003. |
| (IV) |
Full compliance with the applicable
requirements of this subsection must be demonstrated through methods and
procedures approved by Division on or before May 1, 2003. |
|
| (iii) |
All sources of nitrogen oxides
emissions subject to this subsection located in the counties of Bartow,
Carroll, Hall, Newton, Spalding, and Walton and which begin initial operation
after October 1, 1999, shall be in compliance. |
| (iv) |
All sources of nitrogen oxides emissions
subject to this subsection which have potential emissions, expressed as
nitrogen dioxide, not exceeding 50 tons-per-year; were in operation on or
before April 1, 2004; and are located in the counties of Cherokee, Clayton,
Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry,
Paulding and Rockdale shall comply with the following compliance schedule:
| (I) |
A demonstration of appropriate reasonably
available control technology for controlling emissions of nitrogen oxides from
the source must be submitted to the Division no later than October 1, 2004.
Each demonstration is subject to approval, denial, or modification by the
Division. |
| (II) |
A final control plan
and application for a permit to construct for the installation of nitrogen
oxides emission control systems and/or modifications of process or fuel-burning
equipment must be submitted to the Division no later than April 1,
2005. |
| (III) |
On-site construction of
emission control systems and/or modification of process or fuel-burning
equipment must be completed by March 1, 2007. |
| (IV) |
Full compliance with the applicable
requirements of this subsection must be demonstrated through methods and
procedures approved by Division on or before May 1, 2007. |
|
| (v) |
All sources of nitrogen oxide emissions
subject to this subsection located in the counties of Cherokee, Clayton, Cobb,
Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding
and Rockdale and which begin initial operation after April 1, 2004, shall be in
compliance upon startup. |
| (vi) |
All
sources of nitrogen oxide emissions subject to this subsection and located in
Barrow County shall be in compliance by March 1, 2009. |
|
| 4. |
The requirements contained in this
subsection shall not apply to individual equipment at the source which have
potential emissions of nitrogen oxides, expressed as nitrogen dioxide, in
quantities less than a de minimis level of one ton-per-year or to air pollution
control devices which are installed to effect compliance with any requirement
of this Chapter. |
| 5. |
The
requirements contained in this subsection shall not apply to individual
equipment at the source which are subject to subsections (jjj), (lll), (mmm),
or (nnn) of this section 391-3-1-.02(2). |
| 6. |
For the purpose of determining
applicability of this subsection, the emissions of nitrogen oxides from any
source shall exclude all nitrogen oxides emissions subject to subsections
(jjj), (lll), (mmm), or (nnn) of this section 391-3-1-.02(2). |
| 7. |
For all Reasonably Available Control
Technology demonstrations approved or determined pursuant to this subsection,
the Division shall issue a public notice which provides for an opportunity for
public comment and an opportunity for a hearing on the determination. |
| 8. |
All Reasonably Available Control
Technology demonstrations, and any modifications or changes to those
determinations, approved or determined by the Division pursuant to this
subsection shall be submitted by the Division to the U.S. EPA as a revision to
the state implementation plan. No Reasonably Available Control Technology
demonstration, nor any modification or change to a demonstration, approved or
determined by the Division pursuant to this subsection shall revise the state
implementation plan or be used as a state implementation plan credit, until it
is approved by the U.S. EPA as a state implementation plan revision. |
|
| (ccc) |
VOC Emissions from Bulk Mixing Tanks.
| 1. |
After the compliance date specified in
section 4. of this subsection, no person shall let, permit, suffer, or allow
the operation of a mixing tank unless the following requirements for control of
emissions of volatile organic compounds are satisfied:
| (i) |
All portable and stationary mixing tanks
used for the manufacture of any VOC containing material shall be equipped with
covers which completely cover the tank except for an opening no larger than
necessary to allow for safe clearance of the mixer shaft. The tank opening
shall be covered at all times except when operator access is
necessary. |
| (ii) |
Free fall of VOC
containing material into product containers shall be accomplished by
utilization of drop tubes, fill pipes or low-clearance equipment design on
filling equipment unless demonstrated to the Division impractical for a
specific operation. |
| (iii) |
Detergents or non-VOC containing cleaners shall be utilized for both general
and routine cleaning operations of floors, equipment, and containers unless the
cleanup cannot be accomplished without the use of VOC containing
cleaners. |
| (iv) |
All waste solvents
shall be stored in closed containers or vessels, unless demonstrated to be a
safety hazard, and shall be disposed or reclaimed such solvents in a manner
approved by the Division. |
|
| 2. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Mixing
Tanks" means any vessel in which resin, coating or other materials, or any
combination thereof, are added to produce product blend. |
|
| 3. |
The requirements of this subsection shall
apply to facilities with potential VOC emissions exceeding 25 tons-per-year and
located in the counties of Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and Rockdale and to
facilities with potential VOC emissions exceeding 100 tons-per-year and located
in the counties of Barrow, Bartow, Carroll, Hall, Newton, Spalding, and
Walton. |
| 4. |
Compliance Dates.
| (i) |
All sources subject to this subsection
and located in the counties of Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale
shall be in compliance. |
| (ii) |
All
sources subject to this subsection; located in the counties of Bartow, Carroll,
Hall, Newton, Spalding, and Walton; and in operation on or before October 1,
1999, shall be in compliance by May 1, 2003. |
| (iii) |
All sources subject to this subsection;
located in the counties of Bartow, Carroll, Hall, Newton, Spalding, and Walton;
and which begin initial operation after October 1, 1999 shall be in compliance
with this subsection upon startup. |
| (iv) |
All sources subject to this subsection
and located in Barrow County shall be in compliance by March 1, 2009. |
|
|
| (ddd) |
VOC
Emissions from Offset Lithography and Letterpress.
| 1. |
No person shall cause, let, permit,
suffer, or allow the operation of any offset lithography printing facility
unless:
| (i) |
Offset presses utilize fountain
solutions containing 8 percent or less by volume VOCs; and |
| (ii) |
The owner or operator installs and
operates a VOC emission reduction system for all heatset offset printing
operations approved by the Director to have at least a 90 percent reduction
efficiency and a capture system approved by the Director, or an equivalent VOC
emission rate. |
|
| 2. |
No
person shall cause, let, permit, suffer, or allow the operation of any
sheet-fed offset lithography printing facility unless the VOC content of the
on-press (as-applied) fountain solution is:
| (i) |
5.0 percent alcohol or less (by weight);
or |
| (ii) |
8.5 percent alcohol or less
(by weight) and the fountain solution is refrigerated to below 60°F
(15.5°C); or |
| (iii) |
5 percent
alcohol substitute or less (by weight) and no alcohol in the fountain
solution. |
|
| 3. |
Sheet-fed
offset lithography presses with a sheet size of 11 inches by 17 inches or
smaller, and presses with a total fountain solution reservoir of less than 1
gallon are exempt. |
| 4. |
No person
shall cause, let, permit, suffer or allow the operation of any cold-set web-fed
offset lithography printing facility unless the VOC content of the on-press (as
applied) fountain solution is 5 percent alcohol substitute or less (by weight)
and no alcohol in the fountain solution. |
| 5. |
No person shall cause, let, permit,
suffer, or allow the operation of any heatset web-fed offset lithography
printing facility unless the VOC content of the on-press (as-applied) fountain
solutions is:
| (i) |
1.6 percent alcohol or less
(by weight); or |
| (ii) |
3.0 percent
alcohol or less (by weight) and the fountain solution is refrigerated to below
60°F (15.5°C); or |
| (iii) |
5.0
percent alcohol substitute or less (by weight) and no alcohol in the fountain
solution. |
|
| 6. |
For heatset
web-fed offset lithographic and letterpress printing presses, the owner or
operator shall install and operate a VOC emission reduction system for all
dryers with a potential to emit greater than or equal to 25 tons of VOC
emissions per year prior to controls.
| (i) |
Control devices with an initial installation date on or before January 1, 2015,
shall be approved by the Director to have at least a 90 percent reduction
efficiency and a capture system approved by the Director. |
| (ii) |
Control devices with an initial
installation date after January 1, 2015, shall be approved by the Director to
have at least a 95 percent reduction efficiency and a capture system approved
by the Director. |
| (iii) |
For
situations where the inlet concentration is so low that 90 or 95 percent
efficiency cannot be achieved, an outlet concentration of 20 ppmv as hexane on
a dry basis may be used as an alternative. |
| (iv) |
Heatset presses used for book printing
and heatset presses with a maximum web width of 22 inches or less are exempt
from the requirements in of subparagraph 6.(i) through (iii). |
| (v) |
The following materials are exempt from
the requirements of subparagraph 6.(i) through (iii):
| (I) |
sheet-fed or coldset web-fed
inks; |
| (II) |
sheet-fed or coldset
web-fed varnishes; and |
| (III) |
waterborne coatings or radiation (ultra-violet light or electron beam) cured
materials used on offset lithographic or letterpress presses. |
|
|
| 7. |
All cleaners used for
blanket washing, roller washing, plate cleaners, impression cylinder cleaners,
rubber rejuvenators and other cleaners used for cleaning a press, press parts,
or to remove dried ink from areas around a press shall have a VOC composite
vapor pressure less than 10 mm Hg at 20°Celsius or contain less than 70
weight percent VOC. For those tasks that cannot be carried out with low VOC
composite vapor pressure cleaning materials or reduced VOC content cleaning
materials, 110 gallons per year of cleaning materials that do not meet the
requirements of this subsection may be used. |
| 8. |
All cleaning materials and used shop
towels are to be kept in closed containers. |
| 9. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Cleaning Materials" means the materials used to remove excess printing inks,
oils, and residual paper from press equipment. These materials are typically
mixtures of organic (often petroleum-based) solvents. |
| (ii) |
"Fountain Solution" means the mixture of
water and additional ingredients such as etchant, gum arabic and dampening aid
which coats the non-image areas of the printing plate. |
| (iii) |
"Letterpress printing" means a printing
process in which the image area is raised relative to the non-image area and
the past ink is transferred to the substrate directly from the image
surface. |
| (iv) |
"Lithographic
printing" means a printing process where the image and the non-image areas are
chemically differentiated; the image area is oil receptive and non-image area
is water receptive. |
| (v) |
"Offset
lithography printing" means a printing process that transfers the ink film from
the lithographic plate to an intermediary surface (blanket) which then
transfers the ink film to the substrate. |
| (vi) |
"Sheet-fed" refers to the process in
which the substrate is cut into sheets before being printed. |
| (vii) |
"Web-fed" refers to the process in
which the substrate is supplied to the press in the form of rolls. |
|
| 10. |
Applicability. Prior to
January 1, 2015, the requirements of this subparagraph (ddd) shall apply to
facilities at which the potential emissions of volatile organic compounds from
offset lithography printing equal or exceed 25 tons per year and are located in
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1. and 9. |
|
| 11. |
Applicability. Prior to January 1, 2015,
the requirements of this subparagraph (ddd) shall apply to facilities at which
the potential emissions of volatile organic compounds from offset lithography
printing equal or exceed 100 tons per year and are located in Barrow, Bartow,
Carroll, Hall, Newton, Spalding, and Walton Counties as follows:
| (i) |
All applicable facilities shall comply
with the provisions of subparagraphs 1. and 9. |
|
| 12. |
Applicability. Prior to January 1, 2015,
all letterpress printing operations are subject to the applicability and
control requirements of subparagraph 391-3-1-.02(2)(tt). |
| 13. |
Applicability. On and after January 1,
2015, the requirements of this subparagraph (ddd) shall apply to facilities at
which actual emissions of volatile organic compounds from offset lithographic
printing and letter press printing, before controls, equal or exceed 15 pounds
per day (or 2.7 tons per 12-month rolling period) for facilities located in
Barrow, Bartow, Carroll, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Hall, Henry, Newton, Paulding, Rockdale,
Spalding, and Walton Counties as follows:
| (i) |
Individual heatset web offset lithographic printing presses and individual
heatset web letterpress printing presses that have potential emissions of
volatile organic compounds from the dryer, prior to controls, that equal or
exceed 25 tons per year shall comply with the provisions of subparagraph
6; |
| (ii) |
Individual heatset web
offset lithographic printing presses that have potential emissions of volatile
organic compounds from the dryer, prior to controls, that do not equal or
exceed 25 tons per year and are located at facilities at which the potential
emissions of volatile organic compounds from offset lithography printing equal
or exceed 25 tons per year in Cherokee; Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale Counties
shall comply with the provisions of subparagraph 1.(ii); |
| (iii) |
Individual heatset web offset
lithographic printing presses that have potential emissions of volatile organic
compounds from the dryer, prior to controls, that do not equal or exceed 25
tons per year and are located at facilities at which the potential emissions of
volatile organic compounds from offset lithography printing equal or exceed 100
tons per year in Barrow, Bartow, Carroll, Hall, Newton, Spalding, and Walton
Counties shall comply with the provisions of subparagraph 1.(ii); |
| (iv) |
All applicable facilities shall comply
with the provisions of subparagraphs 2., 3., 4., 5., 7., 8., and 9; |
| (v) |
Any physical or operational changes that
are necessary to comply with the provisions specified in subparagraphs 13.(i)
or (iv) are subject to the compliance schedule specified in subparagraph
15. |
|
| 14. |
Applicability:
The requirements of subparagraph 13. will no longer be applicable by the
compliance deadlines if the counties specified in those subparagraphs are
re-designated to attainment for the 1997 National Ambient Air Quality Standard
for ozone prior to January 1, 2015 and such counties continue to maintain that
Standard thereafter. Instead, the provisions of subparagraphs 10., 11., and 12.
will continue to apply on and after January 1, 2015. In the event the 1997
National Ambient Air Quality Standard for ozone is violated in the specified
counties, the requirements of subparagraph 13. will only be reinstated if the
Director determines that the measure is necessary to meet the requirements of
the contingency plan. |
| 15. |
Compliance Schedule:
| (i) |
An application for a
permit to construct and operate volatile organic compound emission control
systems and/or modifications of process and/or coatings used must be submitted
to the Division no later than July 1, 2014. |
| (ii) |
On-site of construction of emission
control systems and/or modification of process or coatings must be completed by
November 1, 2014. |
| (iii) |
Full compliance with the applicable
requirements specified in subparagraphs 13.(i) and (iv) must be completed
before January 1, 2015. |
|
|
| (eee) |
VOC Emissions from Expanded
Polystyrene Products Manufacturing.
| 1. |
Except as provided in sections 2., 3., and 4. of this section, after the
compliance date specified in section 8. of this subsection, no person shall
cause, let, permit, suffer, or allow the VOC emissions from an expandable
polystyrene product manufacturing facility to exceed 0.015 lbs VOC/lb bead
utilized. |
| 2. |
No person shall cause,
let, permit, suffer, or allow the operation of an expandable polystyrene cup
manufacturing facility existing before November 1, 1987 unless the facility has
installed and operates volatile organic compound emission reduction equipment
on the pre-expanders having at least a 90.0 percent reduction efficiency and a
capture system approved by the Director. |
| 3. |
No person shall cause, let, permit,
suffer, or allow the operation of an expandable polystyrene board insulation
manufacturing facility existing before January 1, 1990 unless the facility has
installed and operates volatile organic compound emission reduction equipment
on the pre-expanders so as to achieve at least a 90.0 percent reduction
efficiency and a capture system approved by the Director; or limits VOC
emissions from the entire facility to no greater than 0.0175 lb VOC/lb bead
utilized. |
| 4. |
No person shall cause,
let, permit, suffer, or allow the operation of an expandable polystyrene custom
shape manufacturing facility existing before January 1, 1990, unless the
facility utilizes a batch expander and reduced volatile expandable polystyrene
bead containing no more than 4.5 percent initial VOC content. The monthly
weighted average of all beads used shall not exceed 4.5 percent. |
| 5. |
For the purposes of this subsection, VOC
emitted after the average curing time shall not be considered to be emitted
from the facility. |
| 6. |
For the
purpose of this subsection, the following definitions shall apply:
| (i) |
"Expandable Polystyrene Products
Manufacturing" means the manufacturing of products utilizing expandable
polystyrene bead impregnated with a VOC blowing agent. |
| (ii) |
"Board Insulation Manufacturers" means
producers of thermal insulation, display foam, or floatation products. Thermal
insulation production usually requires densities as specified in ASTM C-578,
the industry standard for both EPS and XPS insulation applications. |
| (iii) |
"Custom Shape Manufacturers" means
producers of a variety of different products ranging in density and size and
based primarily on customer specifications. |
| (iv) |
"Pre-expander" means the system where
initial expansion of the bead occurs. |
| (v) |
"Process" means the point from the
opening of the gaylord to the end of the average curing time. |
|
| 7. |
The requirements of this
subsection shall apply to facilities with potential VOC emissions exceeding 25
tons per year and located in the counties of Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and
Rockdale and to facilities with potential VOC emissions exceeding 100 tons per
year and located in the counties of Barrow, Bartow, Carroll, Hall, Newton,
Spalding, and Walton. |
| 8. |
Compliance
Dates.
| (i) |
All sources subject to this
subsection and located in the counties of Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and
Rockdale shall be in compliance. |
| (ii) |
All sources subject to this subsection
located in the counties of Bartow, Carroll, Hall, Newton, Spalding, and Walton;
and in operation on or before October 1, 1999, shall be in compliance with this
subsection by May 1, 2003. |
| (iii) |
All sources subject to this subsection; located in the counties of Bartow,
Carroll, Hall, Newton, Spalding, and Walton; and which begin initial operation
after October 1, 1999, shall be in compliance with this subsection upon
startup. |
| (iv) |
All sources subject
to this subsection and located in Barrow County shall be in compliance by March
1, 2009. |
|
|
| (fff) |
Particulate Matter Emissions from Yarn Spinning Operations.
| 1. |
No person shall cause, let, permit, suffer
or allow the rate of particulate matter emissions from a yarn spinning
operation with process input rates up to and including 30 tons per hour to
equal or exceed the allowable rate of emissions calculated from the following
equation.
E = 4.1P0.67
where:
E = allowable emission rate in pounds per hour;
P = process input weight of raw or partially processed fiber
in tons per hour.
|
| 2. |
For the
purpose of this subparagraph, the term process, as it applies to the yarn
spinning operation, shall include all of the activities from bale delivery,
bale stripping, carding, drawing, spinning, twisting, to and including winding,
conducted at the facility. |
|
| (ggg) |
Existing Municipal Solid Waste
Landfills.
| 1. |
The provisions of this
subsection apply to each existing municipal solid waste landfill that commenced
construction, reconstruction or modification before May 30, 1991 and has
accepted waste at any time since November 8, 1987, or has additional design
capacity available for future waste deposition. Physical or operational changes
made to an existing municipal solid waste landfill solely to comply with this
subsection are not considered construction, reconstruction, or modification and
would not subject an existing municipal solid waste landfill to the
requirements of 391-3-1-.02(8)(b)72. which are the Federal New Source
Performance Standards for Municipal Solid Waste Landfills. |
| 2. |
Definitions of all Terms used, but not
defined in this subsection, have the meaning given them in 40 CFR Part 60
Subpart WWW, as amended. Terms not defined therein shall have the meaning given
them in the federal Clean Air Act, the Georgia Air Quality Act or 40 CFR Part
60 Subparts A and B.
| (i) |
The word
"Administrator" as used in regulations adopted in this subsection shall mean
the Director of the Georgia Environmental Protection Division. |
|
| 3. |
For the purposes of
implementing the requirements and provisions of the Emission Guidelines of 40
CFR 60 Subpart Cc for Existing Municipal Solid Waste Landfills, each existing
municipal solid waste landfill meeting the conditions of paragraph 1. of this
subsection shall comply with all of the applicable standards, requirements and
provisions of 40 CFR Part 60 Subpart WWW, as amended, which is hereby
incorporated and adopted by reference with the exceptions as follows:
| (i) |
Standards for air emissions from
municipal solid waste landfills. The FR 60.752 apply as stated therein with the
exception of the following:
| (I) |
In lieu of
40 CFR
60.752(a)(2), the following
provision applies:
When an increase in the maximum design capacity of a landfill
exempted from the provisions of
40 CFR
60.752(b) through 40 CFR
60.759 on the basis of the design capacity exemption in
40 CFR
60.752(a) results in a
revised maximum design capacity equal to or greater than 2.5 million megagrams
and 2.5 million cubic meters, the owner or operator shall comply with the
provision of 391-3-1-.02(8)(b)72. which are the Federal New Source Performance
Standards for Municipal Solid Waste Landfills.
|
| (II) |
In lieu of
40 CFR
60.752(b)(2)(i)(B), the
following provision applies:
The collection and control system design plan shall include
any alternatives to the operational standards, test methods, procedures,
compliance measures, monitoring, recordkeeping or reporting provisions of
40 CFR
60.753 through 40 CFR 60.758 proposed by the
owner or operator. In addition, the collection and control system design plan
must specify: (1) the date by which contracts for control system/process
modifications shall be awarded, (which shall be no later than 20 months after
the date the NMOC emissions rate is first calculated to meet or exceed 50
megagrams per year); (2) the date by which on-site construction or installation
of the air pollution control devices(s) or process changes will begin (which
shall be no later than 24 months after the date the NMOC emissions rate is
first calculated to meet or exceed 50 megagrams per year); and (3) the date by
which the construction or installation of the air pollution control devices(s)
or process changes will be complete.
|
|
| (ii) |
Operational standards for collection and control systems. The provisions of
40 CFR
60.753 apply as stated therein. |
| (v) |
Monitoring of operations. The provisions
of 40 CFR
60.756 apply as stated therein. |
| (vi) |
Reporting requirements. The provisions
of 40 CFR
60.757 apply as stated therein with the
exception of the following:
|
| (vii) |
Recordkeeping requirements. The
provisions of 40 CFR
60.758 apply as stated therein. |
| (viii) |
Specifications for active collection
systems. The provisions of 40 CFR 60.759 apply as stated
therein. |
|
|
| (hhh) |
Wood Furniture Finishing and Cleaning Operations.
| 1. |
Each owner or operator of a wood furniture
finishing and cleaning operation shall limit VOC emissions from finishing
operations by:
| (i) |
Using topcoats that
contain no more than 0.8 pounds of VOC per pound of solids, as applied;
or |
| (ii) |
In lieu of complying with
subsection (i), wood furniture finishing operations may comply by:
| (I) |
Using a finishing system of sealers that
contain no more than 1.9 pounds of VOC per pound of solids, as applied;
and |
| (II) |
Using topcoats that
contain no more than 1.8 pounds of VOC per pound of solids, as applied;
or |
|
| (iii) |
For wood
furniture finishing operations that use acid-cured alkyd amino vinyl sealers
and that use acid-cured alkyd amino conversion varnish topcoats:
| (I) |
Using sealers that contain no more than
2.3 pounds of VOC per pound of solids, as applied; and |
| (II) |
Using topcoats that contain no more than
2.0 pounds of VOC per pound of solids, as applied; or |
|
| (iv) |
For wood furniture finishing operations
that do not use acid-cured alkyd amino vinyl sealers and that use acid-cured
alkyd amino conversion varnish topcoats:
| (I) |
Using sealers that contain no more than 1.9 pounds of VOC per pound of solids,
as applied; and |
| (II) |
Using topcoats
that contain no more than 2.0 pounds of VOC per pound of solids, as applied;
or |
|
| (v) |
For wood furniture
finishing operations that use acid-cured alkyd amino vinyl sealers and that do
not use acid-cured alkyd amino conversion varnish topcoats:
| (I) |
Using sealers that contain no more than
2.3 pounds of VOC per pound of solids, as applied; and |
| (II) |
Using topcoats that contain no more than
1.8 pounds of VOC per pound of solids, as applied; or |
|
| (vi) |
Using an averaging approach that
demonstrates the wood furniture finishing operation meets the emission limits
defined in subsections (i), (ii), (iii), (iv) or (v), averaged on a daily basis
throughout the facility; or |
| (vii) |
Using a control system that will achieve an equivalent reduction in emissions
and meet the requirements of subsections (i), (ii), (iii), (iv) or (v) of this
section; or |
| (viii) |
Using a
combination of the methods presented in subsections (i), (ii), (iii), (iv),
(v), (vi), and (vii). |
|
| 2. |
Each owner or operator of a wood furniture finishing and cleaning operation
shall limit VOC emissions by using strippable booth coating materials that
contain no more than 0.8 pounds of VOC per pound of solids, as
applied. |
| 3. |
Each owner or operator
of a wood furniture finishing and cleaning operation shall prepare and maintain
a written work practice implementation plan that defines work practices for
each wood furniture manufacturing operation and addresses each of the topics
specified. The work practice implementation plan shall be submitted to the
Division for approval by the compliance dates contained in section 7. This plan
shall include: an operator training course; a leak inspection and maintenance
plan; a cleaning and washoff solvent accounting system; a spray booth cleaning
plan; a storage plan for finishing, cleaning and washoff materials; an
application equipment requirement plan; a paint line and gun cleaning plan; and
an outline of washoff operations. |
| 4. |
Each owner or operator of a wood furniture
finishing and cleaning operation shall maintain certified product data sheets
for each sealer, topcoat, and strippable booth coating material that is used to
meet the requirements of sections 1. and 2. of this rule. If solvent or other
VOC is added to the finishing material before application, the affected source
shall maintain documentation showing the VOC content of the finishing material
in pounds of VOC-per-pound of solids, as applied. |
| 5. |
For the purpose of this subsection the
following definitions shall apply:
| (i) |
"As
applied" means the VOC and solids content of the finishing material that is
actually used for coating the substrate. It includes the contribution of
materials used for in-house dilution of the finishing material. |
| (ii) |
"Certified product data sheet" means
documentation furnished by a coating supplier or an outside laboratory that
provides the VOC content by percent weight, the solids content by percent
weight, and density of a finishing material, strippable booth coating, or
solvent, measured using the EPA Method 24, or an equivalent or alternative
method. The VOC content should represent the maximum VOC emission potential of
the finishing material, strippable booth coating, or solvent. |
| (iii) |
"Sealer" means a finishing material
used to seal the pores of a wood substrate before additional coats of finishing
material are applied. Washcoats, which are used in some finishing systems to
optimize aesthetics, are not sealers. |
| (iv) |
"Stain" means any color coat having a
solids content by weight of no more than 8.0 percent that is applied in single
or multiple coats directly to the substrate. This includes, but is not limited
to, nongrain raising stains, equalizer stains, sap stains, body stains, no-wipe
stains, penetrating stains, and toners. |
| (v) |
"Strippable booth coating" means a
coating that: (1) is applied to a booth wall to provide a protective film to
receive overspray during finishing operations; (2) that is subsequently peeled
off and disposed; and (3) by achieving (1) and (2), reduces or eliminates the
need to use organic solvents to clean booth walls. |
| (vi) |
"Topcoat" means the last film-building
finishing material applied in a finishing system. Non-permanent final finishes
are not topcoats. |
| (vii) |
"Wood
Furniture" means any product made of wood, a wood product such as rattan or
wicker, or an engineered wood product such as particleboard that is
manufactured under any of the following standard industrial classification
codes: 2434, 2511, 2512, 2517, 2519, 2521, 2531, 2541, 2599, or 5712. |
|
| 6. |
The requirements of this
subsection shall apply to facilities with potential VOC emissions exceeding 25
tons-per-year and located in the counties of Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and
Rockdale and to facilities with potential VOC emissions exceeding 100
tons-per-year and located in the counties of Barrow, Bartow, Carroll, Hall,
Newton, Spalding, and Walton. |
| 7. |
Compliance Dates.
| (i) |
All sources subject to
this subsection and located in the counties of Cherokee, Clayton, Cobb, Coweta,
DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and
Rockdale shall be in compliance. |
| (ii) |
All sources subject to this subsection;
located in the counties of Bartow, Carroll, Hall, Newton, Spalding, and Walton;
and in operation on or before October 1, 1999, shall be in compliance with this
subsection by May 1, 2003. |
| (iii) |
All sources subject to this subsection; located in the counties of Bartow,
Carroll, Hall, Newton, Spalding, and Walton; and which begin initial operation
after October 1, 1999, shall be in compliance with this subsection upon
startup. |
| (iv) |
All sources subject
to this subsection and located in Barrow County shall be in compliance by March
1, 2009. |
|
|
| (iii) |
Hospital/Medical/Infectious Waste Incinerators.
| 1. |
The provisions of this subparagraph apply
to each hospital/medical/infectious waste incinerator (HMIWI) that commenced
construction no later than December 1, 2008 or commenced modification no later
than April 6, 2010 (hereinafter referred to as an "Existing HMIWI"). Physical
or operational changes made to an Existing HMIWI solely to comply with this
subparagraph are not considered construction or modification and would not
subject an Existing HMIWI to the requirements of 391-3-1-.02(8)(b)73.
| (i) |
A combustor is not subject to this
subparagraph during periods when only pathological waste, low-level radioactive
waste, and/or chemotherapeutic waste (all defined in
40 CFR
60.51c ) is burned, provided the owner or
operator of the combustor:
| (I) |
Notifies the
Director of an exemption claim; and |
| (II) |
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. |
|
| (ii) |
Any co-fired combustor (defined in
40 CFR
60.51c ) is not subject to this subparagraph
if the owner or operator of the co-fired combustor:
| (I) |
Notifies the Director of an exemption
claim; |
| (II) |
Provides an estimate of
the relative amounts of hospital waste, medical/infectious waste, and other
fuels and wastes to be combusted; and |
| (III) |
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. |
|
| (iii) |
Any
combustor required to have a permit under section 3005 of the Solid Waste
Disposal Act is not subject to this subparagraph. |
| (iv) |
Any combustor which meets the
applicability requirements under subpart Cb, Ea, or Eb of 40 CFR Part 60 is not
subject to this subparagraph. |
| (v) |
Any pyrolysis unit (defined in
40 CFR
60.51c ) is not subject to this
subparagraph. |
| (vi) |
Cement kilns
firing hospital waste and/or medical/infectious waste are not subject to this
subparagraph. |
|
| 2. |
Each
Existing HMIWI is subject to the permitting requirements of
391-3-1-.03(10)
"Title V Operating Permits." |
| 3. |
Definitions of all Terms used, but not defined in this subparagraph, shall have
the meaning given to them in 40 CFR Part 60, Subpart Ec, as amended on April 4,
2011. Terms not defined therein shall have the meaning given to them in the
federal Clean Air Act or 40 CFR Part 60, Subparts A and B. For the purposes of
this subparagraph the following definitions also apply:
| (i) |
Except as noted, the word "Administrator"
as used in regulations adopted by reference in this subparagraph shall mean the
Director of the Georgia Environmental Protection Division. For subparagraph
(iii)6. the word "Administrator" shall mean the Administrator of the
EPA. |
|
| 4. |
For the purposes
of implementing the requirements and provisions of the Emission Guidelines of
40 CFR 60, Subpart Ce for Existing HMIWIs, each Existing HMIWI shall comply
with the standards, requirements and provisions of 40 CFR Part 60, Subpart Ec,
as amended on April 4, 2011, which is hereby incorporated and adopted by
reference, with the exceptions as follows:
| (i) |
The provisions of 40 CFR
60.50c apply to each Existing HMIWI as stated
therein with the exception of the following:
| (II) |
In lieu of
40 CFR
60.50c(e), the following
provision applies:
Any combustor which meets the applicability requirements
under 40 CFR Part 60 Subparts Cb, Ea, or Eb is not subject to this
subparagraph.
|
|
| (ii) |
Emission
Limits. The provisions of 40
CFR 60.52c apply to each Existing HMIWI as
stated therein with the exception of the following:
| (I) |
In lieu of
40 CFR
60.52c(a), the following
provisions apply:
| I. |
From an affected facility
constructed on or before June 20, 1996 no owner or operator of an Existing
HMIWI shall cause to be discharged into the atmosphere from that affected
facility any gases that contain stack emissions in excess of the applicable
limits found in Table 1B of 40 CFR Part 60, Subpart Ce. |
| II. |
From an affected facility constructed
after June 20, 1996 but no later than December 1, 2008 no owner or operator of
an Existing HMIWI shall cause to be discharged into the atmosphere from that
affected facility any gases that contain stack emissions in excess of the
applicable limits found in the more stringent of the requirements listed in
Table 1B of 40 CFR Subpart Ce and Table 1A of 40 CFR Part 60, Subpart
Ec. |
|
|
| (iii) |
Operator Training. The provisions of
40 CFR
60.53c apply to each Existing HMIWI as stated
therein. |
| (iv) |
Siting Requirements.
The provisions of 40 CFR
60.54c do not apply to an Existing
HMIWI. |
| (v) |
Waste Management Plan.
The provisions of 40 CFR
60.55c apply to each Existing HMIWI as stated
therein. |
| (vi) |
Compliance and
Performance Testing. In lieu of
40 CFR
60.56c, Section 2.117.2 of the Georgia
Department of Natural Resources Procedures for Testing and Monitoring Sources
of Air Pollutants applies to each Existing HMIWI. |
| (vii) |
Monitoring Requirements. In lieu of
40 CFR
60.57c, Section 2.117.3 of the Georgia
Department of Natural Resources Procedures for Testing and Monitoring Sources
of Air Pollutants applies to each Existing HMIWI. |
| (viii) |
Reporting and Record Keeping
Requirements. In lieu of 40
CFR 60.58c, Section 2.117.4 of the Georgia
Department of Natural Resources Procedures for Testing and Monitoring Sources
of Air Pollutants applies to each Existing HMIWI. |
| (ix) |
Table 1B of 40 CFR Part 60, Subpart Ec
does not apply to an Existing HMIWI. |
|
| 5. |
In keeping with subparagraph (iii)4.,
owners and operators of existing HMIWI units must comply with Georgia's state
plan for existing HMIWI units, which is required by 40 CFR Part 60, Subpart Ce.
The owner operator of each existing HMIWI unit shall comply with the
requirements of 391-3-1-.02(2)(iii)4. upon approval of Georgia's state plan for
existing HMIWI units by EPA. |
| 6. |
The
owner of an existing HMIWI unit must contact EPA with respect to the following
subparagraphs (i) through (v) as specified in
40 CFR
60.50c(i).
| (ii) |
Approval of alternative methods of
demonstrating compliance under
40 CFR
60.8 including:
| (I) |
Approval of CEMS for PM, HCl,
multi-metals, and Hg where used for purposes of demonstrating
compliance, |
| (II) |
Approval of
continuous automated sampling systems for dioxin/ furan and Hg where used for
purposes of demonstrating compliance, and |
| (III) |
Approval of major alternatives to test
methods; |
|
| (iii) |
Approval
of major alternatives to monitoring; |
| (iv) |
Waiver of recordkeeping requirements;
and |
|
|
| (jjj) |
NOX Emissions from Electric Utility Steam
Generating Units.
| 1. |
Effective May 1,
1999, through September 30, 1999, no person shall cause, let, permit, suffer,
or allow the emissions of NOX from an affected unit
under this subsection unless:
| (i) |
The
NOX emissions from each affected unit(s) do not exceed
the alternative emission limit established by the Director for the unit(s).
Said alternative emission limits shall be determined by the Division and
established in the Title V Permit for the affected unit(s). In no case shall
the alternative emission limits established pursuant to this section, averaged
over all affected units on a maximum rated heat input capacity basis, be
greater than the average allowable rate specified in subsection
1.(ii). |
| (ii) |
If the person does not
comply with all alternative emission limits established under subsection 1.(i)
above, the person shall demonstrate that the NOX
emissions, averaged over all affected units, do not exceed 0.34 lb/MMBTU heat
input. |
|
| 2. |
Effective May
1, 2000 through September 30, 2002, no person shall cause, let, permit, suffer,
or allow the emissions of NOX from an affected unit
under this subsection unless:
| (i) |
The
NOX emissions from each affected unit(s) do not exceed
the alternative emission limit established by the Director for the unit(s).
Said alternative emission limits shall be determined by the Division and
established in the Title V Permit for the affected unit(s). In no case shall
the alternative emission limits established pursuant to this section, averaged
over all affected units on a maximum rated heat input capacity basis, be
greater than the average allowable rate specified in subsection
2.(ii). |
| (ii) |
If the person does not
comply with all alternative emission limits established under subsection 2.(i)
above, the person shall demonstrate that the NOX
emissions, averaged over all affected units, do not exceed 0.30 lb/MMBTU heat
input. |
|
| 3. |
Effective May
1, 2003, no person shall cause, let, permit, suffer, or allow the emissions of
NOX from an affected unit under this subsection unless:
| (i) |
The NOX emissions
from each affected unit(s) do not exceed the alternative emission limit
established by the Director for the unit(s). Said alternative emission limits
shall be determined by the Division and established in the Title V Permit for
the affected unit(s). In no case shall the alternative emission limits
established pursuant to this section, averaged over all affected units using
the highest 30 consecutive days of actual heat input for 1999, be greater than
the average allowable rate specified in subsection 3.(ii). |
| (ii) |
If the person does not comply with all
alternative emission limits established under subsection 3.(i) above, the
person shall demonstrate that the NOX emissions,
averaged over all affected units, do not exceed 0.13 lb/MMBTU heat
input. |
|
| 4. |
Effective May
1, 2003, through September 30, 2006, no person shall cause, let, permit,
suffer, or allow the emissions of NOX from an affected unit under this
subsection unless:
| (i) |
The NOx emissions from
each affected unit(s) do not exceed the alternative emission limit established
by the Director for the unit(s). Said alternative emission limits shall be
determined by the Division and established in the Title V Permit for the
affected unit(s). In no case shall the alternative emission limits established
pursuant to this section, averaged over all affected units using the highest 30
consecutive days of actual heat input for 1999, be greater than the average
allowable rate specified in subsection 4.(ii). |
| (ii) |
If the person does not comply with all
alternative emission limits established under subsection 4.(i) above, the
person shall demonstrate that the NOX emissions,
averaged over all affected units, do not exceed 0.20 lb/MMBTU heat
input. |
|
| 5. |
Effective May
1, 2007, no person shall cause, let, permit, suffer, or allow the emissions of
NOx from an affected unit under this subsection unless:
| (i) |
The NOx emissions from each affected
unit(s) do not exceed the alternative emission limit established by the
Director for the unit(s). Said alternative emission limits shall be determined
by the Division and established in the Title V Permit for the affected unit(s).
In no case shall the alternative emission limits established pursuant to this
section, averaged over all affected units using the highest 30 consecutive days
of actual heat input for 1999, be greater than the average allowable rate
specified in subsection 5.(ii). |
| (ii) |
If the person does not comply with all
alternative emission limits established under subsection 5.(i) above, the
person shall demonstrate that the NOx emissions, averaged over all affected
units, do not exceed 0.18 lb/MMBTU heat input. |
|
| 6. |
Effective May 1, 2007, no person shall
cause, let, permit, suffer, or allow the emissions of NOx from an affected unit
under this subsection unless:
| (i) |
The NOx
emissions from each affected unit(s) do not exceed the alternative emission
limit established by the Director for the unit(s). Said alternative emission
limits shall be determined by the Division and established in the Title V
Permit for the affected unit(s). In no case shall the alternative emission
limits established pursuant to this section, averaged over all affected units
using the highest 30 consecutive days of actual heat input for 1999, be greater
than the average allowable rate specified in subsection 6.(ii). |
| (ii) |
If the person does not comply with all
alternative emission limits established under subsection 6.(i) above, the
person shall demonstrate that the NOx emissions, averaged over all affected
units, do not exceed 0.17 lb/MMBTU heat input. |
|
| 7. |
The compliance period shall be based on a
30-day rolling average beginning May 1 and ending September 30 of each year.
| (i) |
The first 30-day averaging period shall
begin on May 1. |
| (ii) |
The last
30-day averaging period shall end on September 30. |
| (iii) |
Affected units under this subsection
shall be all coal-fired electric utility steam generating units with a maximum
heat input greater than 250 MMBTU/hr. |
|
| 8. |
The requirements contained in sections 1
and 2 of this subsection shall apply to all such sources located in the
counties of Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth,
Fulton, Gwinnett, Henry, Paulding and Rockdale. The requirements contained in
Section 3 of this subsection shall apply to all such sources located in the
counties of Bartow, Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette,
Floyd, Forsyth, Fulton, Gwinnett, Heard, Henry, Paulding, and Rockdale. The
requirements contained in sections 4 and 5 of this subsection shall apply to
all such sources located in the counties of Bartow, Cherokee, Clayton, Cobb,
Coweta, DeKalb, Douglas, Fayette, Floyd, Forsyth, Fulton, Gwinnett, Heard,
Henry, Monroe, Paulding, Putnam, and Rockdale. The requirements contained in
Section 6 of this subsection shall apply to sources located in Monroe
County. |
|
| (kkk) |
VOC
Emissions from Aerospace Manufacturing and Rework Facilities.
| 1. |
No person shall cause, let, permit,
suffer, or allow the emissions of VOC from the coating of aerospace vehicles or
components to exceed:
| (i) |
2.9 pounds per
gallon of coating, excluding water and exempt solvents, delivered to a coating
applicator that applies primers. For general aviation rework facilities, the
VOC limitation shall be 4.5 pounds per gallon of coating, excluding water and
exempt solvents, delivered to a coating applicator that applies
primers. |
| (ii) |
3.5 pounds per gallon
of coating, excluding water and exempt solvents, delivered to a coating
applicator that applies topcoats (including self-priming topcoats). For general
aviation rework facilities, the VOC limitation shall be 4.5 pounds per gallon
of coating, excluding water and exempt solvents, delivered to a coating
applicator that applies topcoats (including self-priming topcoats). |
| (iii) |
The VOC content limits listed in Table
(kkk) -1 below expressed in pounds per gallon of coating, excluding water and
exempt solvents, delivered to a coating applicator that applies specialty
coatings.
TABLE (kkk) -1 Specialty Coating VOC Limitations
|
Coating Type
|
VOC Content Limit (lb/gal)
|
VOC Content Limit (g/L)
|
|
Ablative Coating
|
5.0
|
600
|
|
Adhesion Promoter
|
7.4
|
890
|
|
Adhesive Bonding Primers:
Cured at 250°F or below
Cured above 250°F
|
7.1
8.6
|
850
1030
|
|
Adhesives:
Commercial Interior Adhesive
Cyanoacrylate Adhesive
Fuel Tank Adhesive
Nonstructural Adhesive
Rocket Motor Bonding Adhesive
Rubber-based Adhesive
Structural Autoclavable Adhesive
Structural Nonautoclavable
Adhesive
|
6.3
8.5
5.2
3.0
7.4
7.1
0.5
7.1
|
760
1,020
620
360
890
850
60
850
|
|
Antichafe Coating
|
5.5
|
660
|
|
Bearing Coating
|
5.2
|
620
|
|
Caulking and Smoothing Compounds
|
7.1
|
850
|
|
Chemical Agent-Resistant Coating
|
4.6
|
550
|
|
Clear Coating
|
6.0
|
720
|
|
Commercial Exterior Aerodynamic Structure
Primer
|
5.4
|
650
|
|
Compatible Substrate Primer
|
6.5
|
780
|
|
Corrosion Prevention Compound
|
5.9
|
710
|
|
Cryogenic Flexible Primer
|
5.4
|
645
|
|
Cryoprotective Coating
|
5.0
|
600
|
|
Dry Lubricative Material
|
7.3
|
880
|
|
Electric or Radiation-Effect Coating
|
6.7
|
800
|
|
Electrostatic Discharge and Electromagnetic
Interference (EMI) Coating
|
6.7
|
800
|
|
Elevated Temperature Skydrol Resistant Commercial
Primer
|
6.2
|
740
|
|
Epoxy Polyamide Topcoat
|
5.5
|
660
|
|
Fire-Resistant (Interior) Coating
|
6.7
|
800
|
|
Flexible Primer
|
5.3
|
640
|
|
Flight-Test Coatings:
Missile or Single Use Aircraft
All Other
|
3.5
7.0
|
420
840
|
|
Fuel- Tank Coating
|
6.0
|
720
|
|
High-Temperature Coating
|
7.1
|
850
|
|
Insulation Covering
|
6.2
|
740
|
|
Intermediate Release Coating
|
6.3
|
750
|
|
Lacquer
|
6.9
|
830
|
|
Maskants:
Bonding Maskant
Critical Use and Line Sealer
Maskant
Seal Coat Maskant
|
10.3
8.5
10.3
|
1,230
1,020
1,230
|
|
Metallized Epoxy Coating
|
6.2
|
740
|
|
Mold Release
|
6.5
|
780
|
|
Optical Anti- Reflective Coating
|
6.3
|
750
|
|
Part Marking Coating
|
7.1
|
850
|
|
Pretreatment Coating
|
6.5
|
780
|
|
Rain Erosion-Resistant Coating
|
7.1
|
850
|
|
Rocket Motor Nozzle Coating
|
5.5
|
660
|
|
Scale Inhibitor
|
7.3
|
880
|
|
Screen Print Ink
|
7.0
|
840
|
|
Sealants:
Extrudable/Rollable/Brushable
Sealant
Sprayable Sealant
|
2.3
5.0
|
280
600
|
|
Silicone Insulation Material
|
7.1
|
850
|
|
Solid Film Lubricant
|
7.3
|
880
|
|
Specialized Function Coating
|
7.4
|
890
|
|
Temporary Protective Coating
|
2.7
|
320
|
|
Thermal Control Coating
|
6.7
|
800
|
|
Wet Fastener Installation Coating
|
5.6
|
675
|
|
Wing Coating
|
7.1
|
850
|
|
| (iv) |
5.2 pounds per gallon of coating, excluding water and exempt solvents,
delivered to a coating applicator that applies Type I chemical milling
maskants. |
| (v) |
1.3 pounds per gallon
of coating, excluding water and exempt solvents, delivered to a coating
applicator that applies Type II chemical milling maskants. |
| (vi) |
The following aerospace activities are
exempt from the coating emission limits in subparagraphs 1.(i) through (v):
touchup coating, aerosol coating, and the application of Department of Defense
classified coatings; coatings used on space vehicles; and facilities that
comply with the low volume usage exemption in subparagraph 10.
|
|
| 2. |
The emission
limitations in subparagraph (kkk) shall be achieved by:
| (i) |
The application of low solvent coating
technology where each and every coating meets the specified applicable
limitation expressed in pounds of VOC per gallon of coating, excluding water
and exempt solvents, stated in subparagraph 1.; or |
| (ii) |
The application of low solvent coating
technology where the monthly volume-weighted average VOC content of each
specified coating type meets the specified applicable limitation expressed in
pounds of VOC per gallon of coating, excluding water and exempt solvents,
stated in subparagraph 1.; averaging is not allowed between primers, topcoats
(including self-priming topcoats), specialty coating types, Type I milling
maskants, and Type II milling maskants or any combination of the above coating
categories; or |
| (iii) |
Control
equipment, including but not limited to incineration, carbon adsorption and
condensation, with a capture system approved by the Director, provided that the
control system has a VOC reduction efficiency of 81 percent or
greater. |
|
| 3. |
Each owner or
operator of an aerospace manufacturing and/or rework operation shall apply all
spray applied non-exempt primers, topcoats, and specialty coatings utilizing
one or more of the spray application techniques specified below:
| (i) |
High-volume low-pressure (HVLP)
spraying; |
| (ii) |
Electrostatic spray
application; |
| (iii) |
Airless spray
application; |
| (iv) |
Air-assisted
airless spray application; or |
| (v) |
Other coating application methods that achieve emission reductions equivalent
to HVLP, electrostatic spray application, airless spray, or air-assisted
airless spray application methods, as determined by the Director. |
|
| 4. |
Each owner or operator of an
aerospace manufacturing and/or rework operation shall ensure that all
application devices used to apply primers, topcoats (including self-priming
topcoats), and specialty coatings are operated according to company procedures,
local specified operating procedures, and/or the manufacturer's specifications,
whichever is most stringent, at all times. Equipment modified by the owner or
operator shall maintain a transfer efficiency equivalent to HVLP, electrostatic
spray application, airless spray application, or air-assisted airless spray
application techniques. |
| 5. |
Each
owner or operator of an aerospace manufacturing and/or rework operation shall
comply with the following housekeeping requirements for any affected cleaning
operation. Aqueous cleaning solvents and hydrocarbon-based solvents which have
a maximum composite vapor pressure of 7 mm Hg at 20°C are exempt from these
requirements.
| (i) |
Solvent-laden cloth, paper,
or any other absorbent applicators used for cleaning shall be placed in bags or
other closed containers upon completing their use. These bags and containers
must be kept closed at all times except when depositing or removing these
materials from the container. The bags and containers used must be of such a
design so as to contain the vapors of the cleaning solvent. Cotton-tipped swabs
used for very small cleaning operations are exempt from this
requirement. |
| (ii) |
All fresh and
spent cleaning solvents, except semi-aqueous solvent cleaners, used in
aerospace cleaning operations shall be stored in closed containers. |
| (iii) |
Conduct the handling and transfer of
cleaning solvents to or from enclosed systems, vats, waste containers, and
other cleaning operation equipment that hold or store fresh spent cleaning
solvents in such a manner that spills are minimized. |
|
| 6. |
Each owner or operator of an aerospace
manufacturing and/or rework operation utilizing hand-wipe cleaning operations
(excluding the cleaning of spray gun equipment performed in accordance with
subparagraph 7.) shall comply with one of the following:
| (i) |
Utilize cleaning solvent solutions that
are classified as an aqueous cleaning solvent and/or a hydrocarbon-based
cleaning solvent with a maximum composite vapor pressure of 7 mm Hg at
20°C. |
| (ii) |
Utilize cleaning
solvent solutions that have a composite vapor pressure of 45 mm Hg or less at
20°C. |
|
| 7. |
Each owner
or operator of an aerospace manufacturing and/or rework operation shall clean
all spray guns used in the application of primers, topcoats (including
self-priming topcoats), and specialty coatings utilizing one or more of the
following techniques:
| (i) |
Enclosed System:
Spray guns shall be cleaned in an enclosed system that is closed at all times
except when inserting or removing the spray gun. Cleaning shall consist of
forcing cleaning solvent through the gun. If leaks are found, repairs shall be
made as soon as practicable, but no later than 15 days after the leak was
found. If the leak is not repaired by the 15th day after detection, the
cleaning solvent shall be removed and the enclosed cleaner shall be shut down
until the leak is repaired or its use is permanently discontinued. |
| (ii) |
Nonatomized Cleaning: Spray guns shall
be cleaned by placing cleaning solvent in the pressure pot and forcing it
through the gun with the atomizing cap in place. No atomizing air is to be
used. The cleaning solvent from the spray gun shall be directed into a vat,
drum, or other waste container that is closed when not in use. |
| (iii) |
Disassembled Spray Gun Cleaning: Spray
guns shall be cleaned by disassembling and cleaning the components by hand in a
vat, which shall remain closed at all times except in use. Alternatively, the
components shall be soaked in a vat, which shall remain closed during the
soaking period and when not inserting or removing components. |
| (iv) |
Atomizing cleaning: Spray guns shall be
cleaned by forcing the cleaning solvent through the gun and directing the
resulting atomized spray into a waste container that is fitted with a device
designed to capture the atomized cleaning solvent emissions. |
|
| 8. |
Each owner or operator of an
aerospace manufacturing and/or rework operation that includes a flush cleaning
operation shall empty the used cleaning solvents each time aerospace parts or
assemblies, or components of a coating unit (with the exception of spray guns)
are flush cleaned into an enclosed container or collection system that is kept
closed when not in use or into a system with equivalent emission control
approved by the Director. Hydrocarbon-based solvents which have a maximum
composite vapor pressure of 7 mm Hg at 20°C and aqueous and semi-aqueous
materials are exempt from the requirements of subparagraph (kkk). |
| 9. |
The following activities are not regulated
by subparagraph (kkk):
| (i) |
Research and
development; |
| (iii) |
Laboratory testing
activities; |
| (v) |
Electrodeposition
(except for the electrodeposition of paints); |
| (vi) |
Composites processing (except for
cleaning and coating of composite parts or components that become part of an
aerospace vehicle or component as well as composite tooling that comes in
contact with such composite parts or components prior to cure); |
| (vii) |
Electronic parts and assemblies (except
for cleaning and topcoating of completed assemblies); |
| (viii) |
Manufacture of aircraft
transparencies; |
| (ix) |
Wastewater
treatment operations; |
| (x) |
Regulated
activities associated with space vehicles designed to travel beyond the limit
of the earth's atmosphere, including but not limited to satellites, space
stations, and the space shuttle; |
| (xi) |
Maintenance and rework of antique
aerospace vehicles and components; |
| (xiii) |
Rework of aircraft or aircraft
components if the holder of the Federal Aviation Administration (FAA) design
approval, or the holder's licensee, is not actively manufacturing the aircraft
or aircraft components; |
| (xiv) |
Parts
and assemblies not critical to the vehicle's structural integrity or flight
performance; |
| (xv) |
Primers,
topcoats, specialty coatings, chemical milling maskants, strippers, and
cleaning solvents that meet the definition of non-VOC material, as determined
from manufacturer's representations, such as in a material safety data sheet or
product data sheet, or testing, except that if an owner or operator chooses to
include one or more non-VOC primer, topcoat, specialty coating, or chemical
milling maskant in averaging under subparagraph 2.(ii); |
| (xvi) |
Primers, topcoats, and specialty
coatings that meet the definition of "classified national security information"
in subparagraph 17.(xvii). |
|
| 10. |
The requirements for primers, topcoats,
specialty coatings, and chemical milling maskants in subparagraphs 1.(i),
1.(ii), 1.(iii), 1.(iv) and 1.(v) do not apply to the use of low-volume
coatings in these categories for which the rolling twelve month total of each
separate formulation used at a facility does not exceed 50 gallons, and the
combined rolling twelve month total of all such primers, topcoats, specialty
coatings, and chemical milling maskants used at a facility does not exceed 200
gallons. Primers, topcoats, and specialty coatings exempted under subparagraphs
9. and 11. are not included in the 50 and 200 gallon limits. |
| 11. |
The following situations are exempt from
the requirements of subparagraphs 3. and 4.:
| (i) |
Any situation that normally requires the
use of an airbrush or an extension on the spray gun to properly reach limited
access spaces; |
| (ii) |
The application
of coatings that contain fillers that adversely affect atomization with HVLP
spray guns and that cannot be applied by any of the application methods
specified in subparagraph 3.; |
| (iii) |
The application of coatings that normally have a dried film thickness of less
than 0.0013 centimeter (0.0005 inches) and that cannot be applied by any of the
application methods specified in subparagraph 3.; |
| (iv) |
The spray application of no more than
3.0 fluid ounces of coating in a single application (i.e., the total volume of
a single coating formulation applied during any one day to any one aerospace
vehicle or component) from a hand-held device with a paint cup capacity that is
equal to or less than 3.0 fluid ounces (89 cubic centimeters). Using multiple
small paint cups or refilling a small paint cup to apply more than 3.0 fluid
ounces under the requirements of subparagraph (kkk) is prohibited. If a paint
cup liner is used in a reusable holder or cup, then the holder or cup must be
designed to hold a liner with a capacity of no more than 3.0 fluid ounces. For
example, a 3.0 ounce liner cannot be used in a holder that can also be used
with a 6.0 ounce liner under the requirements of subparagraph (kkk); |
| (v) |
The use of airbrush application methods
for stenciling, lettering, and other identification markings; |
| (vi) |
The use of hand-held non-refillable
spray (aerosol) can application methods; |
| (vii) |
Touchup and repair
operations; |
| (viii) |
Adhesives,
sealants, maskants, caulking materials, and inks; and |
| (ix) |
The application of coatings that contain
less than 0.17 pounds of VOC per gallon of coating. |
|
| 12. |
The following cleaning operations are
exempt from the requirements of subparagraph 6.:
| (i) |
Cleaning during the manufacture,
assembly, installation, maintenance, or testing of components of breathing
oxygen systems that are exposed to the breathing oxygen; |
| (ii) |
Cleaning during the manufacture,
assembly, installation, maintenance, or testing of parts, subassemblies, or
assemblies that are exposed to strong oxidizers or reducers (e.g., nitrogen
tetroxide, liquid oxygen, or hydrazine); |
| (iii) |
Cleaning and surface activation prior
to adhesive bonding; |
| (iv) |
Cleaning
of electronic parts and assemblies containing electronic parts; |
| (v) |
Cleaning of aircraft and ground support
equipment fluid systems that are exposed to the fluid including air-to-air heat
exchangers and hydraulic fluid systems; |
| (vi) |
Cleaning of fuel cells, fuel tanks, and
confined spaces; |
| (vii) |
Surface
cleaning of solar cells, coating optics, and thermal control
surfaces; |
| (viii) |
Cleaning during
fabrication, assembly, installation, and maintenance of upholstery, curtains,
carpet, and other textile materials used in the interior of the
aircraft; |
| (ix) |
Cleaning of metallic
and non-metallic materials used in honeycomb cores during the manufacture or
maintenance of these cores, and cleaning of the completed cores used in the
manufacture or maintenance of aerospace vehicles or components; |
| (x) |
Cleaning of aircraft transparencies,
polycarbonate, or glass substrates; |
| (xi) |
Cleaning and solvent usage associated
with research and development, quality control, and laboratory
testing; |
| (xii) |
Cleaning operations,
using nonflammable liquids, conducted within five feet of energized electrical
systems. Energized electrical systems means any AC or DC electrical circuit on
an assembled aircraft once electrical power is connected, including interior
passenger and cargo areas, wheel wells, and tail sections; and |
| (xiii) |
Cleaning operations identified as
essential uses under the Montreal Protocol for which the U.S. EPA has allocated
essential use allowances or exemptions. |
|
| 13. |
Each owner or operator of an aerospace
manufacturing and/or rework operation shall submit a monitoring plan to the
Division that specifies the applicable operating parameter value, or range of
values, to ensure ongoing compliance with subparagraph 2.(iii). The monitoring
device shall be installed, calibrated, operated, and maintained in accordance
with the manufacturer's specifications. |
| 14. |
Each owner or operator of an aerospace
manufacturing and/or rework operation utilizing an enclosed spray gun cleaner
shall visually inspect the seals and all other potential sources of leaks at
least once per month. Each inspection shall occur while the spray gun cleaner
is in operation. |
| 15. |
Each owner or
operator of an aerospace manufacturing and/or rework operation utilizing
coatings specified in subparagraph 1. shall maintain the following records:
| (i) |
If following the compliance option in
subparagraph 2.(i), a current list of each coating formulation including the
specific category, VOC content as applied, and the annual amount used for each
coating. |
| (ii) |
If following the
compliance option in subparagraph 2.(ii), a current list of each coating
formulation including the specific category, VOC content as applied, the
monthly amount used for each coating, and the calculated monthly
volume-weighted average VOC content of each specified coating type expressed in
pounds of VOC per gallon of coating, excluding water and exempt
solvents. |
| (iii) |
If following the
compliance option in subparagraph 2.(iii), continuous records demonstrating the
control device was operating at the required destruction efficiency at all
times the coating process was in operation and records demonstrating the
control device was achieving the required destruction efficiency while the
coating process was in operation. |
| (iv) |
If using the low volume usage exemption
in subparagraph 10., a list of each separate formulation and quantity applied
each month and the twelve-consecutive month total of each formulation and the
twelve-consecutive month total of all materials exempted. |
|
| 16. |
Each owner or operator of an aerospace
manufacturing and/or rework operation utilizing cleaning solvents shall
maintain the following records:
| (i) |
Maintain
a current list of hand-wipe and flush cleaning solvents with documentation that
demonstrates that the cleaning solvent complies with one of the composition
requirements in subparagraph 6.(i) and for semi aqueous cleaning solvent used
for flush cleaning. This list shall include the annual amount of each
applicable solvent used. |
| (ii) |
Maintain a current list of hand-wipe cleaning solvents with their respective
vapor pressures or, for blended solvents, VOC composite vapor pressures for all
vapor pressure compliant hand-wipe cleaning solvents listed in subparagraph
6.(ii). This list shall include the monthly amount of each applicable solvent
used. |
| (iii) |
Maintain a current list
of all cleaning solvents with a vapor pressure greater than 45 mm Hg used in
exempt hand-wipe cleaning operations. This list shall identify the applicable
exemption(s) for each process and include the monthly amount of each applicable
solvent used. |
| (iv) |
Maintain a
record of all leaks from enclosed gun cleaners, as found during the monthly
inspection required by subparagraph 14.. The record shall include the
identification of the leaking paint gun cleaner, the date the leak was
discovered, and the date the leak was repaired. |
|
| 17. |
For the purpose of subparagraph (kkk),
the following definitions shall apply:
| (i) |
"Ablative coating" means a coating that chars when exposed to open flame or
extreme temperatures, as would occur during the failure of an engine casing or
during aerodynamic heating. The ablative char surface serves as an insulative
barrier, protecting adjacent components from the heat or open flame. |
| (ii) |
"Adhesion promoter" means a very thin
coating applied to a substrate to promote wetting and form a chemical bond with
the subsequently applied material. |
| (iii) |
"Adhesive bonding primer" means a
primer applied in a thin film to aerospace components for the purpose of
corrosion inhibition and increased adhesive bond strength by attachment. There
are two categories of adhesive bonding primers: primers with a design cure at
250°F or below and primers with a design cure above 250°F. |
| (iv) |
"Aerosol coating" means a coating
applied by means of a hand-held, pressurized container, which is non-refillable
or which utilizes non-refillable propellant canisters and which expels an
adhesive or a coating in a finely divided spray when a valve on the container
is depressed. |
| (v) |
"Aerospace
facility" means any facility that produces, reworks, or repairs in any amount
any commercial, civil, or military aerospace vehicle or component. Regulated
activities include coating, chemical milling, solvent use, and depainting
operations. |
| (vi) |
"Aerospace vehicle
or component" means any fabricated part, processed part, assembly of parts, or
completed unit, with the exception of electronic components, of any
aircraft. |
| (vii) |
"Aircraft
transparency" means the aircraft windshield, canopy, passenger windows, lenses
and other components which are constructed of transparent materials. |
| (viii) |
"Airless and air-assisted airless
spray" mean any coating spray application technology that relies solely on the
fluid pressure of the coating to create an atomized coating spray pattern and
does not apply any atomizing compressed air to the coating before it leaves the
spray gun nozzle. Air-assisted airless spray uses compressed air to shape and
distribute the fan of atomized coating, but still uses fluid pressure to create
the atomized coating. |
| (ix) |
"Antichafe coating" means a coating applied to areas of moving aerospace
components that may rub during normal operations or installation. |
| (x) |
"Antique aerospace vehicle or component"
means an aircraft or component thereof that was built at least 30 years ago. An
antique aerospace vehicle would not routinely be in commercial or military
service in the capacity for which it was designed. |
| (xi) |
"Aqueous cleaning solvent" means a
cleaning solvent in which water is the primary ingredient (greater than 80
percent by weight of cleaning solvent solution as applied must be water).
Detergents, surfactants, and bioenzyme mixtures and nutrients may be combined
with the water along with a variety of additives such as organic solvents
(e.g., high boiling point alcohols), builders, saponifiers, inhibitors,
emulsifiers, pH buffers, and antifoaming agents. Aqueous solutions must have a
flash point greater than 93°C (200°F) (as reported by the manufacturer)
and the solution must be miscible with water. |
| (xii) |
"Bearing coating" means a coating
applied to an antifriction bearing, a bearing housing, or the area adjacent to
such a bearing in order to facilitate bearing function or to protect base
material from excessive wear. A material shall not be classified as a bearing
coating if it can also be classified as a dry lubricative material or a solid
film lubricant. |
| (xiii) |
"Bonding
maskant" means a temporary coating used to protect selected areas of aerospace
parts from strong acid or alkaline solutions during processing for
bonding. |
| (xiv) |
"Caulking and
smoothing compounds" means semi-solid materials which are applied by hand
application methods and are used to aerodynamically smooth exterior vehicle
surfaces or fill cavities such as bolt hole accesses. A material shall not be
classified as a caulking and smoothing compound if it can be classified as a
sealant. |
| (xv) |
"Chemical
agent-resistant coating (CARC)" means an exterior topcoat designed to withstand
exposure to chemical warfare agents or the decontaminants used on these
agents. |
| (xvi) |
"Chemical milling
maskants" means a coating that is applied directly to aluminum components to
protect surface areas when chemical milling the component with a Type I or Type
II etchant. Type I chemical milling maskants are used with a Type I etchant and
Type II chemical milling maskants are used with a Type II etchant. This
definition does not include bonding maskants, critical use and line sealer
maskants, and seal coat maskants. Additionally, maskants that must be used with
a combination of Type I or Type II etchants and any of the above types of
maskants are also not included in this definition. (See also Type I and Type II
etchant definitions.) |
| (xvii) |
"Classified National Security Information" means information that has been
determined pursuant to Executive Order 13526, "Classified National Security
Information," December 29, 2009 or any successor order to require protection
against unauthorized disclosure and is marked to indicate its classified status
when in documentary form. The term "Classified Information" is an alternative
term that may be used instead of "Classified National Security
Information." |
| (xviii) |
"Cleaning
operation" means collectively spray-gun, hand-wipe, and flush cleaning
operations. |
| (xix) |
"Cleaning
solvent" means a liquid material used for hand-wipe, spray gun, or flush
cleaning. This definition does not include solutions that contain no VOCs
(i.e., VOC content less than 1.0 weight percent). |
| (xx) |
"Clear coating" means a transparent
coating applied over a colored opaque coating, metallic substrate, or placard
to give improved gloss and protection to the color coat. In some cases, a
clearcoat refers to any transparent coating without regard to
substrate. |
| (xxi) |
"Coating" means a
material that is applied to a substrate for decorative, protective, or
functional purposes. Such materials include, but are not limited to, paints,
sealants, liquid plastic coatings, caulks, inks, adhesives, and maskants.
Decorative, protective, or functional materials that consist only of protective
oils for metal, acids, bases, or any combination of these substances; paper
film or plastic film which may be precoated with an adhesive by the film
manufacturer; or pre-impregnated composite sheets are not considered coatings
for the purposes of subparagraph (kkk). Materials in handheld non-refillable
aerosol containers, touch-up markers, and marking pens are also not considered
coatings for the purposes of subparagraph (kkk). A liquid plastic coating means
a coating made from fine particle-size polyvinyl chloride (PVC) in solution
(also referred to as a plastisol). |
| (xxii) |
"Coating operation" means using a
spray booth, tank, or other enclosure or any area, such as a hangar, for
applying a single type of coating (e.g., primer); using the same spray booth
for applying another type of coating (e.g., topcoat) constitutes a separate
coating operation for which compliance determinations are performed
separately. |
| (xxiii) |
"Coating unit"
means a series of one or more coating applicators and any associated drying
area and/or oven wherein a coating is applied, dried, and/or cured. A coating
unit ends at the point where the coating is dried or cured, or prior to any
subsequent application of a different coating. It is not necessary to have an
oven or flashoff area to be included in this definition. |
| (xxiv) |
"Commercial exterior aerodynamic
structure primer" means a primer used on aerodynamic components and structures
that protrude from the fuselage, such as wings and attached components, control
surfaces, horizontal stabilizers, vertical fins, wing-to-body fairings,
antennae, landing gear, and doors, for the purpose of extended corrosion
protection and enhanced adhesion. |
| (xxv) |
"Commercial interior adhesive" means
materials used in the bonding of passenger cabin interior components. These
components must meet FAA fireworthiness requirements. |
| (xxvi) |
"Compatible substrate primer" means
either compatible epoxy primer or adhesive primer. |
| (xxvii) |
"Corrosion prevention compound" means
a compound that provides corrosion protection by displacing water and
penetrating mating surfaces, forming a protective barrier between the metal
surface and moisture. Coatings containing oils or waxes are excluded from this
category. |
| (xxviii) |
"Critical use
and line sealer maskant" means a temporary coating, not covered under other
maskant categories, used to protect selected areas of aerospace parts from
strong acid or alkaline solutions such as those used in anodizing, plating,
chemical milling and processing of magnesium, titanium, or high-strength steel,
high-precision aluminum chemical milling of deep cuts, and aluminum chemical
milling of complex shapes. Materials used for repairs or to bridge gaps left by
scrubbing operations are also included in this category. |
| (xxix) |
"Cryogenic flexible primer" means a
primer designed to provide corrosion resistance, flexibility, and adhesion of
subsequent coating systems when exposed to loads up to and surpassing the yield
point of the substrate at cryogenic temperatures (-275°F and
below). |
| (xxx) |
"Cryoprotective
coating" means a coating that insulates cryogenic or subcooled surfaces to
limit propellant boil-off, maintain structural integrity of metallic structures
during ascent or reentry, and prevent ice formation. |
| (xxxi) |
"Cyanoacrylate adhesive" means a
fast-setting, single component adhesive that cures at room temperature. Also
known as "super glue." |
| (xxxii) |
"Depainting operation" means the use of a chemical agent, media blasting, or
any other technique to remove permanent coatings from the outer surface of an
aerospace vehicle or components. The depainting operation includes washing of
the aerospace vehicle or component to remove residual stripper, media, or
coating residue. |
| (xxxiii) |
"Dry
lubricative material" means a coating consisting of lauric acid, cetyl alcohol,
waxes, or other noncross linked resin-bond materials that act as a dry
lubricant. |
| (xxxiv) |
"Electric or
radiation-effect coating" means a coating or coating system engineered to
interact, through absorption or reflection, with specific regions of the
electromagnetic energy spectrum, such as the ultraviolet, visible, infrared, or
microwave regions. Uses include, but are not limited to, lighting strike
protection, electromagnetic pulse (EMP) protection, and radar avoidance.
Coatings that have been designated as "classified" by the Department of Defense
are exempt. |
| (xxxv) |
"Electrostatic
discharge and electromagnetic interference (EMI) coating" means a coating
applied to space vehicles, missiles, aircraft radomes, and helicopter blades to
disperse static energy or reduce electromagnetic interference. |
| (xxxvi) |
"Elevated-temperature
Skydrol-resistant commercial primer" means a primer applied primarily to
commercial-type aircraft that must withstand immersion in phosphate-ester (PE)
hydraulic fluid (Skydrol 500b or equivalent) at the elevated temperature of
150°F for 1,000 hours. |
| (xxxvii) |
"Epoxy polyamide topcoat" means a coating used where harder films are required
or in some areas where engraving is accomplished in camouflage
colors. |
| (xxxviii) |
"Exempt solvent"
means a specified organic compound that has been determined by the EPA to have
negligible photochemical reactivity and is listed in
40 CFR
51.100 and/or
391-3-1-.01(llll). |
| (xxxix) |
"Fire-resistant (interior) coating"
means for civilian aircraft, fire-resistant coatings are used on passenger
cabin interior parts that are subject to the FAA fire-worthiness requirements.
For military aircraft, fire-resistant interior coatings are used on parts that
are subject to the flammability requirements of MIL-STD-1630A and MIL-A-87721.
For space applications, these coatings are used on parts that are subject to
the flammability requirements of SE-R-0006 and SSP 30233. |
| (xl) |
"Flexible primer" means a primer that
meets flexibility requirements such as those needed for adhesive bond primer
fastener heads or on surfaces expected to contain fuel. The flexible coating is
required because it provides a compatible, flexible substrate over bonded sheet
rubber and rubber-type coatings as well as a flexible bridge between fasteners,
skin, and skin-to-skin joints on outer aircraft skins. |
| (xli) |
"Flight test coating" means a coating
applied to aircraft other than missiles or single-use aircraft prior to flight
testing to protect the aircraft from corrosion and to provide required marking
during flight test evaluation. |
| (xlii) |
"Flush cleaning" means the removal of
contaminants such as dirt, grease, and coatings from an aerospace vehicle or
component or coating equipment by passing solvent over, into, or through the
item being cleaned. The solvent may simply be poured into the item cleaned and
then drained, or be assisted by air or hydraulic pressure, or by pumping.
Hand-wipe cleaning operations where wiping, scrubbing, mopping, or other hand
actions used are not included in this definition. |
| (xliii) |
"Fuel tank adhesive" means a
non-rubber based adhesive used to bond components exposed to fuel and which
must be compatible with fuel tank coatings. |
| (xliv) |
"Fuel tank coating" means a coating
applied to fuel tank components for the purpose of corrosion and/or bacterial
growth inhibition and to assure sealant adhesion in extreme environmental
conditions. |
| (xlv) |
"General
aviation" means that segment of civil aviation that encompasses all facets of
aviation except air carriers, commuters, and military. General aviation
includes charter and corporate-executive transportation, instruction, rental,
aerial application, aerial observation, business, pleasure, and other special
uses. |
| (xlvi) |
"General aviation
rework facility" means any aerospace facility with the majority of its revenues
resulting from the reconstruction, repair, maintenance, repainting, conversion,
or alteration of general aviation aerospace vehicles or components. |
| (xlvii) |
"Hand-wipe cleaning operation" means
removing contaminants such as dirt, grease, oil, and coatings from an aerospace
vehicle or component by physically rubbing it with a material such as a rag,
paper, or cotton swab that has been moistened with a cleaning
solvent. |
| (xlviii) |
"High temperature
coating" means a coating designed to withstand temperatures of more than
350°F. |
| (xlix) |
"High volume low
pressure (HVLP) spray equipment" means spray equipment that is used to apply
coating by means of a spray gun that operates at 10.0 psig of atomizing air
pressure or less at the air cap. |
| (l) |
"Hydrocarbon-based cleaning solvent"
means a cleaning solvent that is composed of a mixture of photochemically
reactive hydrocarbons and oxygenated hydrocarbons and have a maximum vapor
pressure of seven mm Hg at 20°C. These cleaners also contain no hazardous
air pollutants. |
| (li) |
"Insulation
covering" means material that is applied to foam insulation to protect the
insulation from mechanical or environmental damage. |
| (lii) |
"Intermediate release coating" means a
thin coating applied beneath topcoats to assist in removing the topcoats in
depainting operations and generally to allow the use of less hazardous
depainting methods. |
| (liii) |
"Lacquer" means a clear or pigmented coating formulated with a nitrocellulose
or synthetic resin to dry by evaporation without a chemical reaction. Lacquers
are resoluble in their original solvent. |
| (liv) |
"Leak" means any visible leakage,
including misting and clouding. |
| (lv) |
"Metallized epoxy coating" means a
coating that contains relatively large quantities of metallic pigmentation for
appearance and/or added protection. |
| (lvi) |
"Mold release" means a coating applied
to a mold surface to prevent the molded piece from sticking to the mold as it
is removed. |
| (lvii) |
"Non-VOC
material" means a primer, topcoat, specialty coating, chemical milling maskant,
cleaning solvent, or stripper that contains no more than 1.0 percent by mass
VOC. |
| (lviii) |
"Nonstructural
adhesive" means an adhesive that bonds nonload bearing aerospace components in
noncritical applications and is not covered in any other specialty adhesive
categories. |
| (lix) |
"Optical
antireflection coating" means a coating with a low reflectance in the infrared
and visible wavelength ranges that is used for antireflection on or near
optical and laser hardware. |
| (lx) |
"Part marking coating" means coatings or inks used to make identifying markings
on material, components, and/or assemblies. These markings may be either
permanent or temporary. |
| (lxi) |
"Pretreatment coating" means an organic coating that contains at least 0.5
percent acids by weight and is applied directly to metal or composite surfaces
provide surface etching, corrosion resistance, adhesion, and ease of
stripping. |
| (lxii) |
"Primer" means
the first layer and any subsequent layers of identically formulated coating
applied to the surface of an aerospace vehicle or component. Primers are
typically used for corrosion prevention, protection from the environment,
functional fluid resistance, and adhesion of subsequent coatings. Primers that
are defined as specialty coatings are not included under this
definition. |
| (lxiii) |
"Rain
erosion-resistant coating" means a coating or coating system used to protect
leading edges of parts such as flaps, stabilizers, radomes, engine inlet
nacelles, etc., against erosion caused by rain impact during flight. |
| (lxiv) |
"Research and development" means an
operation whose primary purpose is for research and development of new
processes and products and that is conducted under the close supervision of
technically trained personnel and is not involved in the manufacture of final
or intermediate products for commercial purposes, except in a de minimis
manner. |
| (lxv) |
"Rocket motor bonding
adhesive" means an adhesive used in rocket motor bonding applications.
|
| (lxvi) |
"Rocket motor nozzle
coating" means a catalyzed epoxy coating system used in elevated temperature
applications on rocket motor nozzles. |
| (lxvii) |
"Rubber-based adhesive" means a quick
setting contact cement that provide a strong, yet flexible bond between two
mating surfaces that may be of dissimilar materials. |
| (lxviii) |
"Scale Inhibitor" means a coating
that is applied to the surface of a part prior to thermal processing to inhibit
the formation of scale. |
| (lxix) |
"Screen print ink" means an ink used in screen printing processes during
fabrication of decorative laminates and decals. |
| (lxx) |
"Sealant" means a material used to
prevent the intrusion of water, fuel, air, or other liquids or solids from
certain areas of aerospace vehicles or components. |
| (lxxi) |
"Seal coat maskant" means an overcoat
applied over a maskant to improve abrasion and chemical resistance during
production operations. |
| (lxxii) |
"Self-priming topcoat" means a topcoat that is applied directly to an uncoated
aerospace vehicle or component for purposes of corrosion prevention,
environmental protection, and functional fluid resistance. More than one layer
of identical coating formulation may be applied to the vehicle or component.
|
| (lxxiii) |
"Semi-aqueous cleaning
solvent" means a solution in which water is a primary ingredient (greater than
60 percent by weight of the solvent solution as applied must be
water). |
| (lxxiv) |
"Silicone
insulation material" means an insulating material applied to exterior metal
surfaces for protection from high temperatures caused by atmospheric friction
or engine exhaust. These materials differ from ablative coatings in that they
are not "sacrificial." |
| (lxxv) |
"Solid film lubricant" means a very thin coating consisting of a binder system
containing as its main pigment material one or more of the following:
molybdenum, graphite, polytetrafluoroethylene (PTFE), or other solids that act
as a dry lubricant between faying surfaces. |
| (lxxvi) |
"Specialty coating" means a coating
that, even though it meets the definition of a primer, topcoat, or self-priming
topcoat, has additional performance criteria beyond those of primers, topcoats,
and self-priming topcoats for specific applications. These performance criteria
may include, but are not limited to, temperature or fire resistance, substrate
compatibility, antireflection, temporary protection or marking, sealing,
adhesively joining substrates, or enhanced corrosion protection. |
| (lxxvii) |
"Specialized function coating" means
a coating that fulfills extremely specific engineering requirements that are
limited in application and are characterized by low volume usage. This category
excludes coatings covered in other Specialty coating categories. |
| (lxxviii) |
"Spray-applied coating operation"
means coatings that are applied using a device that creates an atomized mist of
coating and deposits the coating on a substrate. For the purposes of
subparagraph (kkk), spray-applied coatings do not include the following
materials or activities:
| (I) |
Coatings applied
from a hand-held device with a paint cup capacity that is equal to or less than
3.0 fluid ounces (89 cubic centimeters) in which no more than 3.0 fluid ounces
of coating is applied in a single application (i.e., the total volume of a
single coating formulation applied during any one day to any one aerospace
vehicle or component). Under this definition, the use of multiple small paint
cups and the refilling of a small paint cup to spray apply more than 3.0 fluid
ounces of a coating is a spray-applied coating operation. Under this
definition, the use of a paint cup liner in a reusable holder or cup that is
designed to hold a liner with a capacity of more than 3.0 fluid ounces is a
spray-applied coating operation. |
| (II) |
Application of coating using powder
coating, hand-held non-refillable aerosol containers, or non-atomizing
application technology, including but not limited to paint brushes, rollers,
flow coating, dip coating, electrodeposition coating, web coating, coil
coating, touch-up markers, marking pens, trowels, spatulas, daubers, rags,
sponges, mechanically and/or pneumatic-driven syringes, and inkjet
machines. |
| (III) |
Application of
adhesives, sealants, maskants, caulking materials, and inks.
|
|
| (lxxix) |
"Spray gun"
means a device that atomizes a coating or other material and projects the
particulates or other material onto a substrate. |
| (lxxx) |
"Stripper" means a liquid that is
applied to an aerospace vehicle or component to remove permanent coatings such
as primers, topcoats, and specialty coatings. |
| (lxxxi) |
"Structural autoclavable adhesive"
means an adhesive used to bond load-carrying aerospace components that is cured
by heat and pressure in an autoclave. |
| (lxxxii) |
"Structural nonautoclavable
adhesive" means an adhesive used to bond load-carrying aerospace components
that is cured under ambient conditions. |
| (lxxxiii) |
"Surface preparation" means the
removal of contaminants from the surface of an aerospace vehicle or component
or the activation or reactivation of the surface in preparation for the
application of a coating. |
| (lxxxiv) |
"Temporary protective coating" means a coating applied to provide scratch or
corrosion protection during manufacturing, storage, or transportation. Two
types include peelable protective coatings and alkaline removable coatings.
These materials are not intended to protect against strong acid or alkaline
solutions. |
| (lxxxv) |
"Thermal control
coating" means a coating formulated with specific thermal conductive or
radiative properties to permit temperature control of the substrate. |
| (lxxxvi) |
"Topcoat" means a coating that is
applied over a primer on a aerospace vehicle or component for appearance,
identification, camouflage, or protection. Topcoats that are defined as
specialty coatings are not included under this definition. |
| (lxxxvii) |
"Touch-up and repair coating" means
a coating used to cover minor coating imperfections appearing after the main
coating operation. |
| (lxxxviii) |
"Touch-up and repair operation" means that portion of the coating operation
that is the incidental application of coating used to cover minor imperfections
in the coating finish or to achieve complete coverage. This definition includes
out-of-sequence or out-of-cycle coating. |
| (lxxxix) |
"Type I etchant" means a chemical
milling etchant that contains varying amounts of dissolved sulfur and does not
contain amines. |
| (xc) |
"Type II
etchant" means a chemical milling etchant that is a strong sodium hydroxide
solution containing amines. |
| (xci) |
"Wet fastener installation coating" means a primer or sealant applied by
dipping, brushing, or daubing to fasteners that are installed before the
coating is cured. |
| (xcii) |
"Wing
coating" means a corrosion-resistant topcoat that is resilient enough to
withstand the flexing of the wings. |
|
| 18. |
Applicability.
| (i) |
The requirements of subparagraph (kkk)
shall apply to all aerospace facilities with potential emissions of volatile
organic compounds exceeding 100 tons per year, except in the counties of
Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton,
Gwinnett, Henry, Paulding, and Rockdale, where facilities with potential
emissions of volatile organic compounds exceeding 25 tons per year are subject
to subparagraph (kkk). |
| (ii) |
Effective January 1, 2015, the requirements of subparagraph (kkk) shall apply
to all aerospace facilities with potential emissions of volatile organic
compounds exceeding 25 tons per year in Barrow, Bartow, Carroll, Hall, Newton,
Spalding, or Walton County. The requirements of this subparagraph (ii) will no
longer be applicable if the counties specified in this subparagraph (ii) are
re-designated to attainment for the 1997 National Ambient Air Quality Standard
for ozone prior to January 1, 2015. In the event the 1997 National Ambient Air
Quality Standard for ozone is violated in these counties or the counties
specified in subparagraph (i) above, the requirements of this subparagraph (ii)
will only be reinstated if the Director determines that the measure is
necessary to meet the requirements of the contingency plan. |
|
| 19. |
Compliance Dates.
| (i) |
All aerospace facilities subject to
subparagraph (kkk) and located in the counties of Cherokee, Clayton, Cobb,
Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding
and Rockdale shall be in compliance. |
| (ii) |
All aerospace facilities subject to
subparagraph (kkk); located outside Cherokee, Clayton, Cobb, Coweta, DeKalb,
Douglas, Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding and Rockdale
counties; and in operation on or before October 1, 1999, shall be in compliance
by January 1, 2001. |
| (iii) |
All
aerospace facilities subject to subparagraph (kkk); located outside Cherokee,
Clayton, Cobb, Coweta, DeKalb, Douglas, Fayette, Forsyth, Fulton, Gwinnett,
Henry, Paulding and Rockdale counties; and which begin initial operation after
October 1, 1999, shall be in compliance upon startup. |
| (iv) |
All aerospace facilities subject to
subparagraph (kkk) and utilizing specialty coatings that begin operation after
the effective date of this rule shall be in compliance upon startup. All
aerospace facilities subject to subparagraph (kkk) and utilizing specialty
coatings that are in operation on or before the effective date of this rule
shall be in compliance on or before March 31, 2019. |
|
|
| (lll) |
NOX Emissions From Fuel-Burning Equipment.
| 1. |
No person shall cause, let, suffer,
permit, or allow the emission of nitrogen oxides (NOX)
from an affected unit under this subparagraph that is installed or modified on
or after May 1, 1999, to exceed 30 ppm at 3% oxygen on a dry basis. |
| 2. |
The requirements of this subparagraph
shall apply during the period May 1 through September 30 of each
year. |
| 3. |
All affected units subject
to this subparagraph shall be in compliance on or before May 1, 2000. |
| 4. |
The requirements contained in Subparagraph
1. shall apply to all such affected units as defined in subparagraph 5.(i) that
are located in the counties of Banks, Barrow, Bartow, Butts, Carroll,
Chattooga, Cherokee, Clarke, Clayton, Cobb, Coweta, Dawson, DeKalb, Douglas,
Fayette, Floyd, Forsyth, Fulton, Gordon, Gwinnett, Hall, Haralson, Heard,
Henry, Jackson, Jasper, Jones, Lamar, Lumpkin, Madison, Meriwether, Monroe,
Morgan, Newton, Oconee, Paulding, Pickens, Pike, Polk, Putnam, Rockdale,
Spalding, Troup, Upson, and Walton. |
| 5. |
For the purpose of this subparagraph, the
following definitions apply:
| (i) |
"Affected
Unit" means fuel-burning equipment with a maximum design heat input capacity
equal to or greater than 10 MMBTU/hr and less than or equal to 250
MMBTU/hr. |
| (ii) |
"Annual Capacity
Factor" as used in this subparagraph means the ratio between the actual heat
input to the fuel-burning equipment from fuels other than wood during a period
of 12 consecutive calendar months and the potential heat input to the fuel-
burning equipment from all fuels had the fuel-burning equipment been operated
8,760 hours during that 12-month period at the maximum design heat input
capacity. |
| (iv) |
"Wood" means wood, wood residue, bark,
or any derivative fuel or residue thereof, in any form, including, but not
limited to, sawdust, sanderdust, wood chips, scraps, slabs, millings, shavings,
and processed pellets made from wood or other forest residues. |
|
| 6. |
The requirements of this
subparagraph do not apply to the following:
| (i) |
Fuel-burning equipment, which was
permitted under
391-3-1-.03(1) on
or before May 1, 1999, or which was brought onto the facility on or before May
1, 1999. |
| (ii) |
Duct burners
associated with combined cycle gas turbines. |
| (iii) |
Fuel-burning equipment located in any
of the following counties: Banks, Butts, Chattooga, Clarke, Dawson, Floyd,
Gordon, Haralson, Heard, Jackson, Jasper, Jones, Lamar, Lumpkin, Madison,
Meriwether, Monroe, Morgan, Oconee, Pickens, Pike, Polk, Putnam, Troup, and
Upson that combusts either:
| (II) |
wood in combination with
any other fuel and has annual capacity factor for the other fuels of 10 percent
(0.10) or less and is subject to an enforceable requirement limiting operation
of the equipment to an annual capacity factor for the other fuels of 10 percent
(0.10) or less. |
|
|
|
| (mmm) |
NOX
Emissions from Stationary Gas Turbines and Stationary Engines used to Generate
Electricity.
| 1. |
No person shall cause,
let, suffer, permit, or allow the emission of nitrogen oxides
(NOX), from any stationary gas turbine or any stationary
engine used to generate electricity whose nameplate capacity is greater than or
equal to 100 kilowatts (KWe) and is less than or equal to 25 megawatts (MWe),
to exceed the following:
| (i) |
For stationary
engines in operation before April 1, 2000:
160 ppm @ 15% O2, dry basis
|
| (ii) |
For stationary engines
installed or modified on or after April 1, 2000:
80 ppm @ 15% O2, dry basis
|
| (iii) |
For stationary gas turbines
in operation on or after January 1, 1999 and before October 1, 1999:
42 ppm @ 15% O2, dry basis
|
| (iv) |
For stationary gas turbines
installed or modified on or after October 1, 1999:
30 ppm @ 15% O2, dry basis
|
|
| 2. |
The requirements of
this subsection shall apply during the period May 1 through September 30 of
each year. |
| 3. |
Compliance Dates.
| (i) |
For stationary engines in operation
before April 1, 2000, the affected unit shall comply with the applicable
standard under paragraph 1 above by May 1, 2003. |
| (ii) |
For stationary engines installed or
modified on or after April 1, 2000, the affected unit shall comply with the
applicable standard under paragraph 1 upon startup of the affected
unit. |
| (iii) |
For stationary gas
turbines in operation on or after January 1, 1999 and before October 1, 1999,
the affected unit shall comply with the applicable standard under paragraph 1
above by May 1, 2000. |
| (iv) |
For
stationary gas turbines in installed or modified on or after October 1, 1999,
the affected unit shall comply with the applicable standard under paragraph 1
upon startup of the affected unit. |
|
| 4. |
For the purpose of this subsection, the
following definitions apply:
| (i) |
"Emergency
standby stationary gas turbines and stationary engines" means any stationary
gas turbine or stationary engine that operates only when electric power from
the local utility is not available and which operates less than 200 hours per
year. |
| (iii) |
"Stationary engine" means any spark or
compression ignited internal combustion engine which is either attached to a
foundation at a facility or is portable equipment located at a specific
facility. |
| (iv) |
"Stationary gas
turbine" means any gas turbine that is gas and/or liquid fueled with or without
power augmentation. It is either attached to a foundation at a facility or is
portable equipment located at a specific facility. |
|
| 5. |
Exemptions.
The following units are exempt from the provisions of this
subsection:
| (i) |
Stationary engines
used to power portable rock crushing plants. |
| (ii) |
Stationary engines used directly and
exclusively for agricultural operation necessary for the growing of crops or
the raising of fowl or animals. |
| (iii) |
Stationary gas turbines and stationary
engines not connected to an electrical generator. |
| (iv) |
Laboratory engines or gas turbines used
for research and testing purposes. |
| (v) |
Engines or gas turbines operated by the
manufacturer or distributor of such equipment for purposes of performance
verification and testing at the production facility. |
| (vi) |
Portable, temporary generators used for
special events (i.e. county fair, circus) provided the event does not last more
than 14 days. |
|
| 6. |
The requirements contained in this
subsection shall apply to all such sources located in the counties of Banks,
Barrow, Bartow, Butts, Carroll, Chattooga, Cherokee, Clarke, Clayton, Cobb,
Coweta, Dawson, DeKalb, Douglas, Fayette, Floyd, Forsyth, Fulton, Gordon,
Gwinnett, Hall, Haralson, Heard, Henry, Jackson, Jasper, Jones, Lamar, Lumpkin,
Madison, Meriwether, Monroe, Morgan, Newton, Oconee, Paulding, Pickens, Pike,
Polk, Putnam, Rockdale, Spalding, Troup, Upson, and Walton. |
| 7. |
Emergency standby stationary gas turbines
and stationary engines which meet the definition stated in paragraph 4.(i) are
not subject to the emission limitations of paragraph 1. |
| 8. |
Stationary engines at data centers that
meet all of the following criteria are not subject to the emission limitations
in subparagraph 1:
| (i) |
Operate only for
routine testing and maintenance, when electric power from the local utility is
not available, or during internal system failures; |
| (ii) |
Total annual operation for the engine is
less than 500 hours per year; |
| (iii) |
Operation for routine testing and maintenance during the months of May through
September occurs only between 10 p.m. to 4 a.m. Operation for routine testing
and maintenance during the months of January through April and October through
December may be done during any time of day; and |
| (iv) |
The facility maintains records of all
operation, including the reason for the operation. |
|
|
| (nnn) |
NOX Emissions from Large Stationary Gas Turbines.
| 1. |
No person shall cause, let, suffer,
permit, or allow the emission of nitrogen oxides (NOX),
from any stationary gas turbine whose nameplate capacity is greater than 25
megawatts (MWe), to exceed the following:
| (i) |
For stationary gas turbines permitted under
391-3-1-.03(1)
before April 1, 2000:
30 ppm @ 15% O2, dry basis
|
| (iii) |
For stationary gas turbines permitted
under 391-3-1-.03(1) on
or after April 1, 2000:
6 ppm @ 15% O2, dry basis
|
|
| 2. |
The requirements of
this subsection shall apply during the period May 1 through September 30 of
each year. |
| 3. |
Compliance Dates.
| (i) |
Stationary gas turbines subject to
paragraph 1.(i) above shall comply by May 1, 2003. |
| (ii) |
Stationary gas turbines subject to
paragraph 1.(iii) above shall be in compliance upon startup. |
|
| 5. |
By no later than May 1, 2003,
the owner/operator of an affected unit may submit actual operating performance
data on the affected unit, with the emission reduction technologies, as
approved by the Director, in place and optimized on the affected unit,
sufficient to allow the Director to determine if the NOX
emission limit in subparagraph 1.(i) is technically achievable taking into
account the cost and feasibility of available control options. Based on the
Director's review of the data provided, this rule may be modified. |
| 6. |
The requirements contained in this
subsection shall apply to all such sources located in the counties of Banks,
Barrow, Bartow, Butts, Carroll, Chattooga, Cherokee, Clarke, Clayton, Cobb,
Coweta, Dawson, DeKalb, Douglas, Fayette, Floyd, Forsyth, Fulton, Gordon,
Gwinnett, Hall, Haralson, Heard, Henry, Jackson, Jasper, Jones, Lamar, Lumpkin,
Madison, Meriwether, Monroe, Morgan, Newton, Oconee, Paulding, Pickens, Pike,
Polk, Putnam, Rockdale, Spalding, Troup, Upson, and Walton. |
| 7. |
Exemptions.
The following units are exempt from the provisions of this
subsection provided that they only operate under the following
conditions:
| (i) |
Units operating for
purposes of routine testing, to maintain operability, not to exceed three (3)
hours per month. |
| (ii) |
Units
operating under one of the following emergency conditions. For the purpose of
restarting the steam-electric generating units when all steam-electric
generating units at a facility are down and off-site power is not available
(also known as a "Black Start"). Or, when power problems on the grid would
necessitate implementing manual load shedding procedures for retail customers
(Note: This does not apply to special rate structure conditions). |
|
|
| (ppp) |
Commercial and Industrial Solid Waste Incineration Units.
| 1. |
The provisions of this subparagraph apply
to each commercial and industrial solid waste incinerator (CISWI) unit that
commenced construction on or before June 4, 2010, or commenced modification or
reconstruction after June 4, 2010 but no later than August 7, 2013 (hereinafter
referred to as "existing CISWI unit").
| (i) |
For the purposes of this subparagraph, a "CISWI unit" means any unit that meets
the definition of "Commercial and industrial solid waste incineration (CISWI)
unit" in 40 CFR Part 60, Subpart DDDD. The types of CISWI units include the
following: incinerators; air curtain incinerators; small, remote incinerators;
waste-burning kilns; and energy recovery units. Physical or operational changes
made at an existing CISWI unit solely to comply with this subparagraph are not
considered construction, reconstruction, or modification and would not subject
an existing CISWI unit to the requirements of Georgia rule
391-3-1-.02(8)(b)75. |
| (ii) |
The
following units are exempt from the requirements of this subparagraph:
| (I) |
This subparagraph exempts the types of
units described in subparagraphs I. through XI., but some units are required to
provide notifications. Air curtain incinerators are exempt from the
requirements in this subparagraph except for the provisions in
40 CFR
60.2805,
60.2860, and
60.2870.
| I. |
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 this subpart if
you meet the two requirements specified in subparagraphs I.A. and B.
| A. |
Notify the Administrator that the unit
meets these criteria. |
| B. |
Keep
records on a calendar quarter basis of the weight of pathological waste,
low-level radioactive waste, and/ or chemotherapeutic waste burned, and the
weight of all other fuels and wastes burned in the unit. |
|
| II. |
Municipal waste combustion units.
Incineration units that are subject to 40 CFR Part 60, Subpart Ea (Standards of
Performance for Municipal Waste Combustors); 40 CFR Part 60, Subpart Eb
(Standards of Performance for Large Municipal Waste Combustors); 40 CFR Part
60, Subpart Cb (Emission Guidelines and Compliance Time for Large Municipal
Combustors); 40 CFR Part 60, Subpart AAAA (Standards of Performance for Small
Municipal Waste Combustion Units); or 40 CFR Part 60, Subpart BBBB (Emission
Guidelines for Small Municipal Waste Combustion Units). |
| III. |
Medical waste incineration units.
Incineration units regulated under 40 CFR Part 60, Subpart Ec (Standards of
Performance for Hospital/Medical/Infectious Waste Incinerators for Which
Construction is Commenced After June 20, 1996) or 40 CFR Part 60, Subpart Ce
(Emission Guidelines and Compliance Times for Hospital/Medical/Infectious Waste
Incinerators). |
| IV. |
Small power
production facilities as specified below.
| A. |
The unit qualifies as a small power-production facility under section 3(17)(C)
of the Federal Power Act ( 16 U.S.C.
796(17)(C) ). |
| B. |
The unit burns homogeneous waste (not
including refuse-derived fuel) to produce electricity. |
| C. |
You submit documentation to the Director
and notify the EPA Administrator that the qualifying small power production
facility is combusting homogenous waste. |
|
| V. |
Cogeneration facilities as specified
below.
| A. |
The unit qualifies as a
cogeneration facility under section 3(18)(B) of the Federal Power Act (
16 U.S.C.
796(18)(B) ). |
| B. |
The unit burns homogeneous waste (not
including refuse-derived fuel) to produce electricity and steam or other forms
of energy used for industrial, commercial, heating, or cooling
purposes. |
| C. |
You submit
documentation to the Director and notify the EPA Administrator that the
qualifying cogeneration facility is combusting homogenous waste. |
|
| VI. |
Hazardous waste combustion units. Units
for which you are required to get a permit under section 3005 of the Solid
Waste Disposal Act. |
| VII. |
Materials
recovery units. Units that combust waste for the primary purpose of recovering
metals, such as primary and secondary smelters. |
| VIII. |
Air curtain incinerators. Air curtain
incinerators that burn only the materials listed in paragraphs VIII.A. through
C. of this section are only required to meet the requirements under "Air
Curtain Incinerators'' ( 40
CFR 60.2810 through
60.2870 ).
| A. |
100 percent wood waste. |
| B. |
100 percent clean lumber. |
| C. |
100 percent mixture of only wood waste,
clean lumber, and/or yard waste. |
|
| IX. |
Sewage treatment plants. Incineration
units regulated under Subpart O of 40 CFR Part 60 (Standards of Performance for
Sewage Treatment Plants). |
| X. |
Sewage
sludge incineration units. Incineration units combusting sewage sludge for the
purpose of reducing the volume of the sewage sludge by removing combustible
matter that are subject to 40 CFR Part 60, Subpart LLLL (Standards of
Performance for Sewage Sludge Incineration Units) or 40 CFR Part 60, Subpart
MMMM (Emission Guidelines for Sewage Sludge Incineration Units). |
| XI. |
Other solid waste incineration units.
Incineration units that are subject to 40 CFR Part 60, Subpart EEEE (Standards
of Performance for Other Solid Waste Incineration Units) or 40 CFR Part 60,
Subpart FFFF (Emission Guidelines and Compliance Times for Other Solid Waste
Incineration Units). |
|
|
|
| 2. |
Each existing CISWI unit shall comply with
the model rule standards, requirements, and provisions of 40 CFR Part 60,
Subpart DDDD (Emissions Guidelines and Compliance Times for Commercial and
Industrial Solid Waste Incineration Units), as amended June 23, 2016, which are
hereby incorporated and adopted by reference.
| (i) |
For the purposes of implementing the
requirements and provisions of 40 CFR Part 60, Subpart DDDD, the following
provisions are hereby incorporated and adopted by reference:
| (I) |
40 CFR
60.2575 through 40 CFR 60.2615, Increments of
Progress except that in 40
CFR 60.2580, "table 1 of this subpart" is
replaced with " 391-3-1-.02(2)(ppp)6. "; and in
40 CFR
60.2595, "for that increment of progress in
table 1 of this subpart" is replaced with "in 391-3-1-.02(2)(ppp)6.
". |
| (II) |
40 CFR
60.2620 through 40 CFR 60.2630, Waste
Management Plan except that in
40 CFR
60.2625, "table 1 of this subpart for
submittal of the final control plan" is replaced with " 391-3-1-.02(2)(ppp)6.
". |
| (IX) |
40 CFR
60.2740 through
60.2800, Recordkeeping and
Reporting with the exception of the following:
| I. |
In
40 CFR
60.2755, "table 1 of this subpart for
submittal of the final control plan" is replaced with " 391-3-1-.02(2)(ppp)6.
". |
| II. |
In lieu of
40 CFR
60.2795(b)(1) &(2):
| A. |
Within 60 days after the date of
completing each performance test as required by this subparagraph, each owner
or operator must submit the results of the performance test required by this
subparagraph to the Director. Performance test results required to be submitted
to EPA must follow provision 40 CFR
60.2795(b)(1). |
| B. |
Within 60 days after the date of
completing each CEMS performance evaluation test, as defined in this
subparagraph and required by this subparagraph, each owner or operator must
submit the relative accuracy test audit (RATA) data, to the Director. RATA data
required to be submitted to EPA must follow provision
40 CFR
60.2795(b)(2). |
|
|
| (XI) |
40 CFR
60.2810 through
60.2870, Air Curtain Incinerators
except that in 40 CFR
60.2820, "table 1 of this subpart" is
replaced with " 391-3-1-.02(2)(ppp)6. "; and in
40 CFR
60.2835, "for that increment of progress in
table 1 of this subpart" is replaced with " 391-3-1-.02(2)(ppp)6. ". |
| (XIII) |
40 CFR Part 60 Subpart DDDD Tables 2
through 9 except that in Table 5, in the Due Date column for the Waste
Management Plan report, "table 1 for the submittal of the final control plan"
is replaced with " 391-3-1-.02(2)(ppp)6. ". |
|
|
| 3. |
The owner of an existing CISWI unit must
contact EPA with respect to the authorities specified in
40 CFR Part
60.2542. |
| 4. |
Each Existing CISWI unit is subject to the
permitting requirements of
391-3-1-.03(10)
"Title V Operating Permits". |
| 5. |
Definitions of all terms used, but not defined in this subparagraph, shall have
the meaning given to them in 40 CFR Part 60, Subpart DDDD, as amended. Terms
not defined therein shall have the meaning given to them in the federal Clean
Air Act or 40 CFR Part 60, Subparts A and B. For the purposes of this
subparagraph the following definitions also apply:
| (i) |
Except as noted, the word "Administrator"
as used in regulations adopted by reference in this subparagraph shall mean the
Director of the Georgia Environmental Protection Division. For subparagraph
(ppp)3. the word "Administrator" shall mean the Administrator of the
EPA. |
| (ii) |
The term "Air Curtain
Incinerator" as used in regulations adopted in this subparagraph shall mean an
incinerator that operates by forcefully projecting a curtain of air across an
open chamber or pit in which combustion occurs. Incinerators of this type can
be constructed above or below ground and with or without refractory walls and
floor. (Air curtain incinerators are not to be confused with conventional
combustion devices with enclosed fireboxes and controlled air technology such
as mass burn, modular, and fluidized bed combustors.) |
| (iii) |
The term "You" means the owner or
operator of a CISWI unit subject to this rule. |
|
| 6. |
In keeping with subparagraph (ppp)2.,
owners and operators of existing CISWI units must comply with Georgia's state
plan for existing CISWI units, which is required by 40 CFR Part 60, Subpart
DDDD. The owner operator of each existing CISWI unit shall comply with the
requirements of 391-3-1-.02(2)(ppp)2. upon approval of Georgia's state plan for
existing CISWI units by EPA. |
|
| (qqq) |
VOC Emissions from Extruded
Polystyrene Products Manufacturing Utilizing a Blowing Agent.
| 1. |
No person shall cause, let, permit,
suffer, or allow the three-month rolling average VOC emissions from an existing
extruded polystyrene (XPS) products manufacturing facility that utilizes a
blowing agent, to exceed 0.8 lbs per 100 lbs of raw material processed during
any month. Compliance with this limit shall be calculated as follows:
Final VOC Emissions = (Facility VOC Emissions)/(Raw
Material)
|
| 2. |
No person shall
cause, let, permit, suffer, or allow the three-month rolling average VOC
emissions from any new or reconstructed extruded polystyrene (XPS) products
manufacturing facility that utilizes a blowing agent, to exceed 0.3 lbs per 100
lbs of raw material processed during any month. Compliance with this limit
shall be calculated as follows:
Final VOC Emissions = (Facility VOC Emissions)/(Raw
Material)
|
| 3. |
For the
purposes of subparagraphs 1 and 2 above, the VOC emissions from the product
manufacturing operations and the post-manufacturing operations are to be
calculated as follows:
|
B =
|
A - C - D
|
|
A =
|
VOC Blowing Agent Used (pounds per any consecutive
three-month period)
|
|
B =
|
VOC Emissions Primary Extrusion, Roll Storage, and
Thermoforming (Uncontrolled) for each control device (pounds per any
consecutive three-month period)
|
|
C =
|
VOC in the Reclaim Material (pounds per any
consecutive three-month period)
|
|
D =
|
VOC in the Final Product (pounds per any consecutive
three-month period)
|
|
E =
|
VOC Emissions from Finished Goods Warehouses
(Uncontrolled) (pounds per any consecutive three-month period)
|
|
OCE =
|
Overall Control Efficiency of a control device =
[(CE)/100*(DE)/100*(UT)/100]
|
|
CE =
|
Capture Efficiency of a Control Device (percent VOC
captured)
|
|
DE =
|
Destruction Efficiency of a Control Device (percent
VOC destruction)
|
|
UT =
|
Percentage of operating time for the control device
(for the consecutive three-month period)
|
|
n =
|
Total number of control device systems associated
with primary extrusion, roll storage, and thermoforming
|
|
m =
|
Total number of control device systems associated
with the reclaim system
|
|
p =
|
Total number of control device systems associated
with the finished goods warehouses
|
|
| 4. |
Exemptions.
| (i) |
The provisions of
subparagraphs 1 and 2 above shall not apply to Extruded Polystyrene Products
Manufacturing facilities at any single site that processes less than 200 pounds
per day of raw material. |
| (ii) |
The
provisions of subparagraphs 1and 2 above shall not apply to any single site
that contains one or more XPS post-manufacturing operations and does not
contain any XPS product manufacturing operations. |
|
| 5. |
Any owner or operator subject to
subparagraphs 1 or 2 above shall maintain a record of operations, including but
not limited to the amount of raw material processed, the equipment used, the
type of blowing agent used, and operation and maintenance records of all VOC
emission control systems such as temperature, pressure, flow rate, and other
m | | |
