| (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 800ºF; and |
| (iii) |
it has a secondary burner to control
smoke and/or odors and maintain a temperature of at least 1500ºF 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 Hospital/Medical/Infectious Waste Incinerators for Which
Construction is Commenced After June 20, 1996," 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 for Which Construction is
Commenced On or Before June 20, 1996," 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/Industrial/Solid Waste Incinerators for Which
Construction is Commenced After November 30, 1999," as amended; |
| (vii) |
any incinerator subject to Section
391-3-1-.02(2)(ppp) of the Georgia Rules for Air Quality Control
"Commercial/Industrial/Solid Waste Incinerators" for Which Construction is
Commenced On or Before November 30, 1999," 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 Constructed On or Before October 14, 2010" 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 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., 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 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. |
|
|
| (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 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. |
|
|
| (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 50ºF; 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 100ºF, 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 1200ºF 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 194ºF. 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 194ºF. |
| (ii) |
"Baked coating" means a coating that is cured at a temperature at or above
194ºF. |
| (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 250ºF; 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 200ºF, 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
400ºF 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
1000ºF 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 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 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.-13ºF when condensing VOC of vapor pressure greater
than 5.8 psi, measured at 68ºF; II.5ºF when condensing VOC of vapor pressure greater
than 2.9 psi, measured at 68ºF; III.32ºF when condensing VOC of vapor pressure greater
than 1.5 psi, measured at 68ºF; IV.50ºF when condensing VOC of vapor pressure greater
than 1.0 psi, measured at 68ºF; V.77ºF when condensing VOC of vapor pressure greater
than 0.5 psi, measured at 68ºF. |
| (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 68ºF; and |
| II. |
Install pressure/vacuum conservative
vents set on all storage tanks that store VOC with vapor pressure greater than
1.5 psi at 68ºF 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 68ºF. |
| (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 50ºF 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. |
|
| (zz) |
Gasoline Dispensing
Facilities--Stage II.
| 1. |
After January
1, 1993, no person may construct or reconstruct a gasoline dispensing facility
unless the gasoline dispensing facility is equipped and operating with a vapor
recovery system to recover the displacement vapors from the vehicle's gasoline
storage tank. |
| 2. |
The requirements
of this subsection shall not apply to facilities used exclusively for the
fueling of implements of husbandry or individual dispensers used exclusively
for the initial fueling and/or re-fueling of vehicles equipped with onboard
refueling vapor recovery (ORVR) equipment. Furthermore, the gasoline volume
dispensed into vehicles equipped with ORVR shall not be considered in any
determination of applicability of this subsection. |
| 3. |
For the purpose of this subsection, the
following definitions shall apply:
| (i) |
"Approved Stage II vapor recovery system" means a Stage II vapor recovery
system that has demonstrated 95 percent by weight or greater VOC control
efficiency by:
| (I) |
Stage II gasoline vapor
recovery system properly certified under the CARB vapor recovery certification
procedures effective on or before March 31, 2001, or a Stage II gasoline vapor
recovery system properly certified under the CARB enhanced vapor recovery
certification procedures effective April 1, 2001; 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; or |
| (II) |
Tested and approved by the Department
using appropriate CARB test procedures and methods; or equivalent test
procedures and methods approved by the Environmental Protection Division and
EPA, and conducted by the Division or by a third party approved by the
Division. |
|
| (ii) |
"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. |
| (iii) |
"CARB" means the
California Air Resources Board, Sacramento, CA 96812. |
| (iv) |
"Division" means the Environmental
Protection Division of the Georgia Department of Natural Resources. |
| (v) |
"Fill Cap" means a cap that fits over the
stationary gasoline storage tank riser which contains the submerged fill pipe
and that is used to prevent contaminants from entering the tank and as a
secondary measure to prevent the release of gasoline vapors. |
| (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) |
"Independent small business marketer of gasoline" means an owner engaged in the
marketing of gasoline who receives more than 50 percent of his annual income
from refining or marketing of gasoline, unless such a person:
| (II) |
Controls, is controlled by, or is under
common control with, a refiner; or |
| (III) |
Is otherwise directly or indirectly
affiliated with a refiner or with a person who controls, is controlled by, or
is under common control with a refiner, unless the sole affiliation referred to
herein is by means of a supply contract or an agreement or contract to use a
trademark, trade name, service mark, or other identifying symbol or name owned
by such refiner or any such person. |
|
| (ix) |
"Operator" means any person who operates
a facility utilizing gasoline dispensing equipment and receives income from
sale of gasoline at such facility. |
| (x) |
"Owner" means the person who owns the
gasoline dispensing equipment which transfers gasoline from a stationary
gasoline storage tank, which shall include but not be limited to the gasoline
dispensers, hoses, nozzles, breakaways, and vapor piping. |
| (xi) |
"Reconstruction" means the replacement
of any stationary gasoline storage tank and/or the replacement of all gasoline
dispensers. |
| (xii) |
"Refiner" means a
person engaged in producing gasoline, kerosene, distillate fuel oils,
lubricants, or other products through distillation of petroleum or through the
redistillation, cracking, or reforming of unfinished petroleum derivatives, and
whose total refinery capacity (including the refinery capacity of any person
who controls, is controlled by, or is under common control with, such refiner)
is 65,000 barrels per day or greater. |
| (xiii) |
"Stage II controls" means a gasoline
vapor recovery system which recovers vapors during the refueling of motor
vehicles. |
| (xiv) |
"Vapor cap" means
the cap that fits over the stationary gasoline storage tank riser which carries
vapors from the storage tank to the delivery vessels during the transfer of
gasoline in two-point Stage I vapor recovery systems and that is used to
prevent contaminants from entering the storage tank and as a secondary measure
to prevent the loss of gasoline vapors. |
|
| 4. |
Once a gasoline dispensing facility
becomes subject to this rule, it will continue to be subject even if the
gasoline throughput rate falls below the applicability threshold until the
facility decommissions its approved Stage II vapor recovery system as specified
under paragraph 21. of this subsection. |
| 5. |
After the compliance date specified in
paragraph 7. of this subsection, no person may transfer or cause or allow the
transfer of gasoline from stationary storage tanks at gasoline dispensing
facilities subject to regulation under
391-3-1-.02 (2)(zz) to any vehicle
gasoline tank unless the gasoline dispensing facility is equipped with an
approved vapor recovery system to recover the displaced vapors from the
vehicle's gasoline tank. Beginning on May 1, 2014, gasoline dispensing
facilities subject to regulation under
391-3-1-.02 (2)(zz) may decommission
its approved Stage II vapor recovery system as specified under paragraph 21. of
this subsection. Once a facility has decommissioned its Stage II vapor recovery
system, it is no longer required to recover the displaced vapors from vehicle
gasoline tanks. |
| 6. |
The requirements
contained in this subsection shall apply to all gasoline dispensing facilities
located in the counties of Cherokee, Clayton, Cobb, Coweta, DeKalb, Douglas,
Fayette, Forsyth, Fulton, Gwinnett, Henry, Paulding, and Rockdale. |
| 7. |
The compliance date for existing gasoline
dispensing facilities required to install Stage II controls shall be as
follows:
| (i) |
Facilities which began
construction or reconstruction after November 15, 1990, must comply by no later
than May 15, 1993. |
| (ii) |
Facilities
constructed before November 15,1990, which are not owned by independent small
business marketers and which have an average monthly throughput rate of 100,000
gallons or more of gasoline per month, must comply by no later than November
15, 1993. |
| (iii) |
Facilities
constructed before November 15, 1990, which are not owned by independent small
business marketers and which have an average monthly throughput rate between
10,000 and 100,000 gallons of gasoline per month, must comply by no later than
November 15, 1994. |
| (iv) |
Multiple
facilities owned by a single independent small business marketer and which have
an average monthly throughput rate of more than 50,000 gallons of gasoline per
month, the following schedule applies:
| (I) |
no
less than 33 percent of such facilities must comply by no later than November
15, 1993. |
| (II) |
no less than 66
percent of such facilities must comply by no later than November 15,
1994. |
| (III) |
all or 100 percent of
such facilities must comply by no later than November 15, 1995. |
|
| (v) |
A single facility owned by a
single independent small business marketer of gasoline and which has an average
monthly volume throughput rate of more than 50,000 gallons of gasoline per
month, must comply no later than November 15, 1994. |
|
| 8. |
The following facilities are exempted from
Stage II requirements:
| (i) |
All gasoline
dispensing facilities that dispense no more than 10,000 gallons of gasoline per
month. |
| (ii) |
Any gasoline dispensing
facility constructed or reconstructed prior to November 15, 1995 that dispenses
up to and including 50,000 gallons and less per month and is owned by an
independent small business marketer of gasoline. |
| (iii) |
Any new gasoline dispensing facility or
gasoline dispensing facility having undergone reconstruction that commenced or
recommenced dispensing of gasoline to motor vehicles after December 31,
2011. |
|
| 9. |
Stage II vapor
recovery systems at each gasoline dispensing facility shall be certified as
being properly installed and properly functioning. Certification, compliance
testing, recertification, and decommissioning shall be made by a trained,
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 any test to determine
vapor tightness for a vapor recovery system for certification, compliance
testing, recertification, or decommissioning purposes. |
| 10. |
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 initially required
certification testing, compliance testing, recertification, or decommissioning
testing, the owner or operator shall notify the Division at least five days in
advance as to when the testing will occur and what party will conduct the
testing. |
| 11. |
Compliance reporting
and recertification testing of the vapor recovery system shall be required
according to the following schedule:
| (i) |
Compliance reporting shall be required within twelve months of the original
certification test and annually thereafter. This report shall be submitted to
the Division and shall include results of either:
| (I) |
a vapor tightness test and other
functional test(s) as required by the Division; or |
| (II) |
a procedure or procedures equivalent to
(I) as approved by the Division. |
|
| (ii) |
Recertification will be required every
five years or upon major system modification or replacement. This
recertification shall include a leak check test and other functional tests that
are required by the Division. A major system modification is considered to be
replacing, repairing or upgrading 75 percent or more of a facility's Stage II
vapor recovery system. The percent measure is based on the cost of a total
system replacement at the time of replacement, repair or upgrading. |
|
| 12. |
Facilities equipped with Stage
II vapor controls 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 and is in proper working
order. |
| (ii) |
Inspection of all Stage
II related files to ensure that the facility has complied with maintenance
requirements and other record keeping requirements such as inspection,
compliance and volume reports. |
| (iii) |
Observation of the use of equipment by
facility operators and the public. These inspections shall include dispensing
units, processors and handling units and any other systems-related equipment
such as Stage I equipment. |
| (iv) |
A
functional test of the required shut off or flow prohibiting
mechanisms. |
| (v) |
A Dynamic Back
pressure test (DBT); if applicable to the system. |
| (vi) |
Other compliance tests as deemed
necessary by the Division. |
| (vii) |
Verification that the facility has complied with the Leak Test (LT) and the
Liquid Blockage Test (LBT) requirements. |
| (viii) |
Inspection for labels, signs and/or
other public information. |
|
| 13. |
Each owner or operator shall ensure that
at least one facility representative receives training and instruction in the
operation and maintenance of the specific Stage II vapor recovery system in use
at the facility. Such training shall be provided by the qualified instructor on
the specific Stage II equipment. The trained facility representative shall
instruct other appropriate facility employees as to the purpose and operating
procedures of the system. Training shall include, but is not limited to, the
following:
| (i) |
Purposes and effects of the
Stage II vapor control program; |
| (ii) |
Equipment operation and function
specific to the facility's system; |
| (iii) |
Maintenance schedules and requirements
for the facility's equipment; |
| (iv) |
Equipment manufacturer contacts (names, addresses and phone numbers) for parts
and service. |
|
| 14. |
Each
owner or operator shall post operating instructions conspicuously on the front
of each gasoline dispenser using the Stage II vapor recovery system. These
instructions shall, at a minimum, include:
| (i) |
A clear description of how to correctly dispense gasoline using the
system; |
| (ii) |
A warning to not
attempt continued refueling after automatic shutoff of the system (an
indication that the vehicle fuel tank is full); and |
| (iii) |
A telephone number to be used to report
to the station owner or company repair representative any problems experienced
with the system. |
|
| 15. |
The
owner or operator shall maintain the Stage II 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
paragraph, the following is a list of equipment defects in Stage II vapor
recovery systems that substantially impair the effectiveness of the systems in
reducing refueling vapor emissions:
| (i) |
Absence or disconnection of any component that is a part of the approved
system; |
| (ii) |
A vapor hose that is
crimped or flattened such that the vapor passage is blocked, or the pressure
drop through the vapor hose exceeds by a factor of 2 or more the value as
certified in the approved system; |
| (iii) |
A nozzle boot that is torn in one or
both of the following ways:
| (I) |
A
triangular-shaped or similar tear more than 1/2 inch on a side, or a hole more
than 1/2 inch in diameter; or |
| (II) |
A slit more than 1 inch in length; |
|
| (iv) |
A faceplate or flexible cone on a
balance nozzle or a nozzle in a vacuum assist type system, that is damaged such
that the capability to achieve a seal with a fill pipe interface is affected
for at least 1/4 of the circumference of the faceplate (accumulated); |
| (v) |
A nozzle shutoff mechanism that
malfunctions in any manner; |
| (vi) |
Vapor return lines, including such components as swivels, anti-recirculation
valves, and underground piping, that malfunction or are blocked, or are
restricted such that the pressure drop through the line exceeds by a factor of
2 or more the value as certified in the approved system; |
| (vii) |
A vapor processing unit that is
inoperative; |
| (viii) |
A vacuum
producing device that is inoperative; |
| (ix) |
Pressure/vacuum relief valves, vapor
check valves, or dry breaks that are inoperative; |
| (x) |
Any equipment defect that is identified
by the Division as substantially impairing the effectiveness of the system in
reducing refueling vapor emissions; or |
|
| 16. |
Upon identification of any of the defects
as described above, the owner or operator shall tag "out-of-order" all
dispensing equipment for which vapor recovery has been impaired. The tagged
equipment shall be rendered inoperable and the tag(s) shall not be removed
until the defective equipment has been repaired, replaced, or adjusted as
necessary. The Division shall be promptly notified by U.S. Mail as to the
corrective actions taken by the company's repair representative with regards to
major repairs. Hoses, nozzles, nozzle boots and other routine repairs are
exempted from this notification. |
| 17. |
The owner or operator shall inspect all
nozzles and nozzle boots or faceplates on a daily basis. |
| 18. |
Owners or operators of facilities subject
to Stage II vapor control shall maintain, at the facility, any applicable
permits or licenses to operate the facility or specific system current at all
times. All required records shall be made readily available for the Division's
inspection. Certification and test results which verify that the Stage II vapor
recovery system meets the requirements shall be maintained for five years or
until it is decommissioned, whichever is less. |
| 19. |
The following records shall be maintained
for two years or until the Stage II vapor recovery system is decommissioned,
whichever is less:
| (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. |
| (iii) |
Gasoline throughput records which will
allow the average monthly gasoline throughput rate to be continuously
determined. |
| (iv) |
Inspection results
including self-inspection weekly summaries. |
| (v) |
Records of operator employee training for
current employees. |
|
| 20. |
Record disposal may be approved by the Division upon a written request by the
owner or operator of the 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
subsection. |
| 21. |
Owners or operators
of gasoline dispensing facilities subject to the Stage II vapor recovery
control requirements shall fully decommission their Stage II vapor recovery
systems in accordance with the provisions of this subsection.
| (i) |
Beginning May 1, 2014, owners or
operators of gasoline dispensing facilities with Stage II vapor recovery
systems may commence decommissioning of those systems. Decommissioning of the
Stage II vapor recovery systems shall be completed no later than April 30,
2016. |
| (ii) |
An existing Stage II
vapor recovery system shall be decommissioned only in accordance with the
requirements in this Subparagraph.
| (I) |
The
entire existing Stage II vapor recovery system shall be fully decommissioned
prior to the Stage II system no longer being operated and maintained as
required by this rule and the terms and conditions of the system's currently
applicable CARB Executive Order and Approval Letters. |
| (II) |
The gasoline dispensers connected to the
Stage II vapor recovery system shall be taken out of service prior to the start
of decommissioning and shall not be brought back into service to dispense
gasoline until the requirements in this Subparagraph have been met. |
| (III) |
If the Stage II vapor recovery system
has any liquid-collection points and liquid is present, the liquid must be
removed and disposed of properly. If the liquid-collection point has a tube
leading back to the submersible pump, the tube must be disconnected at the
submersible pump, and the tube sealed properly so that it is vapor tight. A
plug must be installed in the vacuum pump to seal the vacuum port. As an
alternative to sealing the tube, the tube may be removed completely as long as
the opening for the tube in the liquid-collection point is sealed so that it is
vapor tight. The liquid-collection point cap shall create a vapor tight seal
when placed on the liquid-collection point. |
| (IV) |
If the Stage II vapor recovery system
includes a vapor pump for each fueling position, the vapor pump shall be
disabled or removed. |
| (V) |
If the
Stage II vapor-recovery system includes a centrally-located vacuum pump, the
vacuum-pumping mechanism shall be removed. After removing the vacuum-generating
mechanism, the vapor piping that was attached to the vapor pump must be sealed
so that it is vapor tight. |
| (VI) |
The
below-grade vapor piping shall be disconnected from the dispenser at a point
that is at or below the level of the base of the dispenser. The below-grade
vapor piping shall be properly sealed so that it is vapor tight. |
| (VII) |
The lower end of the vapor piping
inside of each dispenser cabinet shall be sealed so that it is vapor
tight. |
| (VIII) |
The vapor recovery
piping connection at the storage tank shall be disconnected if it can be
disconnected without excavation. If the vapor recovery piping is disconnected
at the storage tank, the dispenser and tank side of the vapor piping shall be
sealed so that it is vapor tight. |
| (IX) |
A rubber cap held in place by a hose
clamp shall not be used to seal the vapor piping for any of the requirements in
this subparagraph. |
| (X) |
If Stage II
vapor recovery system operating instructions are posted on dispensers, the
operating instructions shall be removed. |
|
| (iii) |
Within 30 calendar days of meeting the
requirements in Subparagraph 21.(ii), a pressure decay test and tie-tank test
shall be conducted to insure that the Stage I vapor recovery system is vapor
tight and the storage tank vents are still functional. The pressure decay test
shall be conducted in accordance with and meet the performance requirements in
the CARB test procedure TP-201.3 "Determination of 2 Inch WC Static Pressure
Performance of Vapor Recovery Systems of Dispensing Facilities" adopted on
April 12, 1996, and amended on March 17, 1999. The tie-tank test shall be
conducted in accordance with and meet the performance requirements in the CARB
test procedure TP201.3C "Determination of Vapor Piping Connections to
Underground Gasoline Storage Tanks" (Tie-Tank Test) adopted on March 17,
1999. |
| (iv) |
The gasoline dispensing
facility owner or operator shall notify the Division a minimum of five business
days, as defined by the Division, prior to the testing required for the
decommissioning of the Stage II vapor recovery system as specified by
Subparagraph 21.(iii). The owner or operator shall use and complete the
notification form provided by the Division. |
| (v) |
The gasoline dispensing facility owner or
operator shall submit a complete test report containing the results of the
testing required by Subparagraph 21.(iii) within 30 days of the test date to
the Division. The test report form shall be provided by the Division and must
be used and completed in its entirety by the owner or operator. The report
shall include results of all tests conducted for decommissioning of the Stage
II vapor recovery system. |
| (vi) |
The
gasoline dispensing facility owner or operator shall maintain the following
records on-site for two years after decommissioning:
| (I) |
Contracts and invoices associated with
decommissioning of the Stage II vapor recovery system. |
| (II) |
Contracts, invoices, and test results
for required testing for decommissioning of the Stage II vapor recovery
system. |
|
| (vii) |
A gasoline
dispensing facility is considered fully decommissioned once the following
conditions have been met:
| (I) |
All of the
requirements in Subparagraph 21.(ii) have been met; |
| (II) |
All tests required in Subparagraph
21.(iii) have been conducted and performance requirements met; and |
| (III) |
Test report(s) as required in
Subparagraph 21.(v) have been submitted to and approved by the
Division. |
|
|
|
| (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 60ºF
(15.5ºC); 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
60ºF (15.5ºC); 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 20ºCelsius 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 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 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 Constructed on or Before June 20, 1996.
| 1. |
The provisions of this subsection apply to
each hospital/medical/infectious waste incinerator (HMIWI) that commenced
construction, reconstruction or modification on or before June 20, 1996
(hereinafter referred to as an "Existing HMIWI"). Physical or operational
changes made to an Existing HMIWI solely to comply with this subsection are not
considered construction, reconstruction, or modification and would not subject
an Existing HMIWI to the requirements of
391-3-1-.02 (8)(b)73.
| (i) |
Any owner or operator of an incinerator
which is a co-fired combustor that continuously complies with the limits and
requirements specified in sections (I), (II), (III) of this paragraph is not
subject to any other provision of this subsection.
| (I) |
In any calendar quarter, the total amount
of waste incinerated that meets the definition of "Hospital or
Medical/Infectious Waste" shall not exceed 10 percent of the total amount of
waste burned during that same period. |
| (II) |
A log shall be maintained for recording
the weight of each charge of waste loaded into the incinerator. Each entry in
the log shall indicate the weight of waste that is Hospital or
Medical/Infectious waste and the weight of all other waste charged. The log
shall be summarized at the end of each quarter showing the total amount of each
waste that has been incinerated during that period. |
| (III) |
By the effective date of this
subsection or prior to incinerating any Hospital or Medical/Infectious waste,
the owner or operator shall submit an initial certification to the Division
stating that the incinerator will be operated in accordance with the limits and
requirements specified in subparagraphs 1.(i)(I) and (II) of this subsection.
|
|
|
| 2. |
The Owner
or Operator of each Existing HMIWI shall submit the initial notification
report, on forms provided, to the Division by no later than March 30,
1999. |
| 3. |
This subsection shall
become effective on the date Georgia's State Implementation Plan for Existing
HMIWIs (hereinafter referred to as the "State HMIWI Plan") receives federal
approval, but no later than March 15, 1999. |
| 4. |
The Owner or Operator of each Existing
HMIWI shall comply with all requirements in paragraph 7. of this subsection,
including the requirements to conduct an initial performance test demonstrating
compliance with the emissions limits and establishing operational parameters,
on or before the date 1 year after federal approval of the State HMIWI Plan,
but no later than March 15, 2000. |
| 5. |
Each Existing HMIWI is subject to the
permitting requirements of
391-3-1-.03 (10) "Title V Operating
Permits." Each owner and operator of an Existing HMIWI shall submit a Title V
application to the Division by March 15, 2000. |
| 6. |
Definitions of all Terms used, but not
defined in this subsection, shall have the meaning given to them in 40 CFR Part
60, Subpart Ec, 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 subsection the following definitions also apply:
| (i) |
The term "Administrator" as used in
regulations adopted in this subsection shall mean the Director of the Georgia
Environmental Protection Division. |
| (ii) |
The term "EPA" as used in regulations
adopted in this subsection shall mean the Georgia Environmental Protection
Division. |
|
| 7. |
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, 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, Eb, or Ec (standards or guidelines for
certain municipal and new medical waste combustors) is not subject to this
Subpart. |
|
| (ii) |
The definition for "Modification or
Modified HMIWI" found in 40
CFR 60.51c does not apply to an Existing
HMIWI. |
| (iii) |
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
provision applies:
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 1 of
40 CFR
60.33e(a). Table 1 of
40 CFR
60.33e(a) is hereby
incorporated and adopted by reference. |
|
| (iv) |
Operator Training. An Operator of an
Existing HMIWI must meet the requirements as outlined in the State HMIWI Plan
to be considered qualified to operate an HMIWI. The provisions of
40 CFR
60.53c apply as stated therein with the
exception of the following:
| (I) |
In lieu of
40 CFR
60.53c(h)(10)(i)(1), the
following provision applies:
The initial review of the information listed in paragraph (h)
of 60.53c shall be conducted within 12 months after federal approval of the
State HMIWI Plan or prior to assumption of responsibilities affecting HMIWI
operation, whichever date is later, but no later than March 15, 2000. |
|
| (v) |
Siting
Requirements. The provisions of
40 CFR
60.54c do not apply to an Existing
HMIWI. |
| (vi) |
Waste Management Plan.
The provisions of 40 CFR
60.55c apply to each Existing HMIWI as stated
therein. |
| (vii) |
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. |
| (viii) |
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. |
| (ix) |
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. |
|
|
| (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)
|
|
Ablative Coating
|
5.0
|
|
Adhesion Promoter
|
7.4
|
|
Adhesive Bonding Primers:
|
|
|
Cured at 250ºF or below
|
7.1
|
|
Cured above 250ºF
|
8.6
|
|
Adhesives:
|
|
|
Commercial Interior Adhesive
|
6.3
|
|
Cyanoacrylate Adhesive
|
8.5
|
|
Fuel Tank Adhesive
|
5.2
|
|
Nonstructural Adhesive
|
3.0
|
|
Rocket Motor Bonding Adhesive
|
7.4
|
|
Rubber-based Adhesive
|
7.1
|
|
Structural Autoclavable Adhesive
|
0.5
|
|
Structural Nonautoclavable Adhesive
|
7.1
|
|
Antichafe Coating
|
5.5
|
|
Bearing Coating
|
5.2
|
|
Caulking and Smoothing Compounds
|
7.1
|
|
Chemical Agent-Resistant Coating
|
4.6
|
|
Clear Coating
|
6.0
|
|
Commercial Exterior Aerodynamic Structure
Primer
|
5.4
|
|
Compatible Substrate Primer
|
6.5
|
|
Corrosion Prevention Compound
|
5.9
|
|
Cryogenic Flexible Primer
|
5.4
|
|
Cryoprotective Coating
|
5.0
|
|
Dry Lubricative Material
|
7.3
|
|
Electric or Radiation-Effect Coating
|
6.7
|
|
Electrostatic Discharge and Electromagnetic
Interference (EMI) Coating
|
6.7
|
|
Elevated Temperature Skydrol Resistant Commercial
Primer
|
6.2
|
|
Epoxy Polyamide Topcoat
|
5.5
|
|
Fire-Resistant (Interior) Coating
|
6.7
|
|
Flexible Primer
|
5.3
|
|
Flight-Test Coatings:
|
|
|
Missile or Single Use Aircraft
|
3.5
|
|
All Other
|
7.0
|
|
Fuel-Tank Coating
|
6.0
|
|
High-Temperature Coating
|
7.1
|
|
Insulation Covering
|
6.2
|
|
Intermediate Release Coating
|
6.3
|
|
Lacquer
|
6.9
|
|
Maskants:
|
|
|
Bonding Maskant
|
10.3
|
|
Critical Use and Line Sealer Maskant
|
8.5
|
|
Seal Coat Maskant
|
10.3
|
|
Metallized Epoxy Coating
|
6.2
|
|
Mold Release
|
6.5
|
|
Optical Anti-Reflective Coating
|
6.3
|
|
Part Marking Coating
|
7.1
|
|
Pretreatment Coating
|
6.5
|
|
Rain Erosion-Resistant Coating
|
7.1
|
|
Rocket Motor Nozzle Coating
|
5.5
|
|
Scale Inhibitor
|
7.3
|
|
Screen Print Ink
|
7.0
|
|
Sealants:
|
|
|
Extrudable/Rollable/Brushable Sealant
|
2.3
|
|
Sprayable Sealant
|
5.0
|
|
Silicone Insulation Material
|
7.1
|
|
Solid Film Lubricant
|
7.3
|
|
Specialized Function Coating
|
7.4
|
|
Temporary Protective Coating
|
2.7
|
|
Thermal Control Coating
|
6.7
|
|
Wet Fastener Installation Coating
|
5.6
|
|
Wing Coating
|
7.1
|
|
| (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 for the coating emission limits in paragraphs 1.(i) through (v):
touchup, aerosol, and DOD classified coatings; coatings used on space vehicles;
and facilities that comply with the low volume usage exemption in paragraph 10.
| 2. |
The emission limitations in this
subsection 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 section 1 of this
subsection; 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 section 1 of this subsection; 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 non-exempt primers and
topcoats utilizing one or more of the application techniques specified below:
| (i) |
Flow/curtain application; |
| (ii) |
Dip coat application; |
| (v) |
Cotton-tipped swab application; |
| (vi) |
Electrodeposition (dip)
coating; |
| (vii) |
High-volume
low-pressure (HVLP) spraying; |
| (viii) |
Electrostatic spray application;
or |
| (ix) |
Other coating application
methods that achieve emission reductions equivalent to HVLP or electrostatic
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 and topcoats (including self-priming topcoats) 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 or electrostatic 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 20ºC 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
section 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
20ºC. |
| (ii) |
Utilize cleaning
solvent solutions that have a composite vapor pressure of 45 mm Hg or less at
20ºC. |
|
| 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 20ºC and aqueous and semi-aqueous
materials are exempt from the requirements of this Section. | | | | |
