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Background on Federal Air Emissions Regulations
While this database focuses on state programs, there are federal requirements that may apply in addition to
these state programs. Click on the program name for additional detail.
New Source Performance Standards (NSPS) - Impose specific performance standards on
a variety of specific technologies. The only likely requirement to impact small electric generating units is a
limit on NOx emissions from turbines.
New Source Review (NSR) - Case by case permitting and emission control requirements
triggered by new construction or modification. Requirements vary depending on the location and air quality attainment
status of a region. Imposes control requirements called BACT or LAER. This program
is a federal program that is administered by the states with EPA oversight.
Title V - Requires states to issue a separate federal operating permit for sources
that exceed certain emission thresholds. This is also a federal program administered by the state. The operating
permit does not set control requirements, but does triggers monitoring and reporting requirements. However, some
states use the Title V thresholds as triggers for other control requirements.
MACT - Sets limits for sources emitting hazardous air pollutants. Only impacts "major"
hazardous polluters.
New Source Performance Standards (NSPS)
The 1970 Clean Air Act called for the EPA to establish minimum federal standards of air pollution control for new
equipment in a variety of industries. These New Source Performance Standards (NSPS) were developed mainly in the
1970s and 1980s for over 70 different source types, ranging from power plants to dry cleaners. The standards are
supposed to be reviewed and updated periodically but that process has been spotty.
Any new plant equipment that fits the description of an NSPS source type is required to meet the NSPS emission
limits and perform additional monitoring, testing, recordkeeping, and other requirements listed in the NSPS for
that source type. The NSPS also applies to modifications of existing sources that result in an increase in emissions
rate or emissions of a new pollutant. Due to the specific wording of the language on modifications, NSPS is almost
never triggered by a modification. The result is that equipment installed since the implementation of the rule
meets NSPS standards but older equipment often does not.
In 1979, EPA promulgated an NSPS for stationary gas turbines. The details of this NSPS are given in 40
CFR 60 Subpart GG. The rule has been amended multiple times over the past few years.
Most of the amendments are related to monitoring and testing requirements. However, the EPA
did set new emission limits for stationary combustion turbines in July 2006. The revised NSPS
regulations released this summer apply to stationary combustion turbines with a heat input at peak
load equal to or greater than 10 MMBtu per hour that commence construction, modification, or
reconstruction after February 18, 2005. Turbine owners or operators can meet concentration-based
or output-based standards. The standards can be found in this Federal Register Notice.
New turbines firing natural gas, for electric generation, with a heat input at peak load of less
than or equal to 50 MMBtu/hr must meet a NOx emission standard of 42 ppm at 15% oxygen. The 50 MMBtu/h
category peak heat input is based on the fuel input to a 23% efficient 3.5 MW combustion turbine.
The lowest NOx emission standard under the revised regulations is for new, modified, or reconstructed
turbines firing natural gas, with a heat input at peak load greater than 850 MMBtu/h. These units must
meet an emission limit of 15 ppm at 15% oxygen. The 850 MMBtu/h category peak heat input is based on the
fuel input to a 44% efficient 110 MW combustion turbine. The highest NOx emission standard under the
modified regulations is 150 ppm and applies to new turbines firing fuels other than natural gas used
for mechanical drive and modified or reconstructed turbines, both categories must have a heat input at
peak load less than or equal to 50 MMBtu/h. The 150 ppm NOx limit also applies to the following
turbines with a peak load heat input of less than or equal to 30 MW of output: turbines located North
of the Artic Circle, operating at less than 75% of peak load, modified and reconstructed offshore
turbines, and turbines operating at temperatures less than 0 degrees Fahrenheit.
Most turbines available today can achieve NOx emissions of 25-42 ppm or less without add-on controls.
Thus the NSPS is not typically a controlling regulation for turbines. The NSPS also set forth conditions
to limit emissions of sulfur dioxide. The emission standard for SO2 is the same for all turbines
regardless of fuel usage or size. Units cannot emit into the air any gases which contain SO2 in excess of
110 ng/J (0.90 lb/MWh) gross energy output for turbines located in continental areas and 780 ng/J
(6.2lb/MWh gross energy output for non-continental areas. Turbines can either meet the SO2 limit or a
limit on the sulfur content of the fuel. The fuel sulfur content limit is 26 ng SO2/J (0.060 lbSO2/MMBtu)
heat input in continental areas and 180 ng SO2/J (0.42 lb SO2/MMBtu) heat input in non-continental areas.
In addition to the emission limits in the NSPS for gas turbines, there are requirements for initial
testing of NOx and sulfur dioxide emissions, monitoring requirements if water injection is used for
NOx control, and guidelines for reporting of any noncompliance with emission limits.The NSPS was supposed
to be updated every 8 years, but the NSPS for gas turbines had not been modified since 1982 before it
was modified in 2006.
In 2006, the EPA also finalized NSPS for stationary compression ignition (CI) internal combustion
engines (ICE), this rule became effective in September of 2006. For CI ICE, Affected sources are any CI
ICE whose construction or modification commenced after July 11, 2005. The format of the final standard
is an output-based emission standard for PM, NOX, CO, and NMHC in units of emissions mass per unit work
performed (grams per kilowatt-hour (g/ KW-hr)) and smoke standards as a percentage. The standards are
modeled after the EPA’s standards for nonroad and marine diesel engines. Emission limits are designated
by pre-2007 model year engine standards and model year 2007 and later standards. Engines based on
their size and model year typically do not have to meet emission limits for every regulated pollutant:
PM, CO, NOx, and NMHC. Emission limits can be found in the
Federal Register Notice.
New Source Review
The national clean air strategy is based on the requirement that all geographic areas meet the National Ambient
Air Quality Standards (NAAQS). NAAQS were established in 1977 for six criteria pollutants, which include:
· Lead
· Nitrogen dioxide (NO2)
· Particulate matter (PM)
· Sulfur dioxide (SO2)
· Carbon monoxide (CO)
· Ground level ozone (O3)
One of the most important tools used to insure that the NAAQS are met is the requirement for pre-construction permitting
of new stationary sources that emit the criteria pollutants or their precursors. Construction or modification of
an emission source may trigger the requirement for a preconstruction review by an air pollution control agency
under the federal or state New Source Review (NSR) program. Technically the new source permitting program comprises
the prevention of significant deterioration (PSD) and the nonattainment new source review programs however, the
entire program is generically referred to as NSR. The permitting process determines what pollution controls will
be required.
NSR Major Source Thresholds for NOx
(tons per year)
|
Nonattainment Classification
|
New Source
|
Modified Source
|
Offset Ratio
|
|
Ozone Transport Region
|
100 tpy
|
40 tpy
|
1.15:1 |
|
Moderate
|
100 tpy
|
40 tpy
|
1.15:1 |
|
Serious
|
50 tpy
|
25 tpy
|
1.2:1 |
|
Severe
|
25 tpy
|
25 tpy
|
1.3:1 |
|
Extreme
|
10 tpy
|
25 tpy
|
1.5:1 |
|
Attainment Area
|
100/250 tpy
|
40 tpy
|
N/A |
Prevention of Significant Deterioration
In attainment areas, the new source requirements are addressed by the Prevention of Significant Deterioration (PSD)
program. PSD review is triggered by the construction of a "major" source of emissions or a modification
of an existing major source that causes a "significant" increase in emissions. "Major" for
new PSD of NOx sources means 250 tpy except for the sources listed in the table below, for which the threshold is 100
tpy. An individual turbine or engine, by itself, may not have high enough emissions to trigger PSD, but a whole
facility could. The measure of emissions is based on potential to emit at full output and utilization - emissions
at full output for an entire year.
PSD Source Categories with 100 TPY Major Source Thresholds
| Fossil fuel-fired steam electric power plants > 250 MMBtu/hr input |
Fossil fuel-fired steam electric power plants > 250 MMBtu/hr input |
| Fossil fuel boilers (or combinations) total > 250 MMBtu/hr heat input |
Petroleum storage and transfer units > 300,000 bbl storage capacity |
| Municipal incinerators > 250 tons/day refuse |
Coal cleaning plants |
| Portland cement plants |
Primary zinc smelters |
| Iron and steel mill plants |
Primary aluminum ore reduction plants |
| Primary copper smelters |
Hydrofluoric acid plants |
| Sulfuric acid plants |
Nitric acid plants |
| Kraft pulp mills |
Petroleum refineries |
| Lime plants |
Carbon black plants/TD>
|
| Primary lead smelters |
Phosphate rock processing plants |
| Coke oven batteries |
Sintering plants |
| Fuel conversion plants |
Secondary metal production plants |
| Charcoal production plants |
Glass Fiber processing plants |
| Taconite ore processing plants |
Secondary metal production plants |
The PSD threshold for modifications is an emissions increase of 40 tpy. This is important in the common case
where a DG unit is added to an existing facility. If the facility is already a major source, the major modification
trigger would be 40 tpy, rather than 100 or 250 tpy. This would make a significant difference in the potential
for triggering PSD review.
BACT
If a source triggers PSD, then the owner must identify the appropriate level of emission controls. In attainment
areas, the standard is Best Available Control Technology (BACT). BACT means the control technology that achieves
the greatest emission reduction within a preset cost per ton of reduction criterion. As a result of its structure,
BACT is a changing standard, which becomes more stringent over time as new, more effective and lower cost control
technologies become available. BACT for a specific application can be defined only in the context of current demonstrated
technology and for a specific application. Because BACT determinations are completely site-specific, one cannot
cite general BACT requirements. However, there have been BACT determinations as low as 2 to 5 ppm NOx for turbines
(larger than 25 MW) and as low as 0.07 g NOx/hp-hr for engines. A sample of BACT requirements can be viewed at
the EPA's website at: http://cfpub1.epa.gov/rblc/htm/bl02.cfm
Nonattainment New Source Review
The table below shows the major source thresholds for nonattainment areas, which are more stringent than in attainment
areas. The NSR program requires that major new or modified emission sources located in nonattainment areas offset
potential increases in NOx emissions. Offsets are required of new sources as a means of reducing their direct impact
on air quality. An offset is a reduction in another facility's actual air emissions in exchange for pollution that
would be created by a new source. A new source offset is called an emissions reduction credit (ERC) and is usually
expressed in tons per year. ERCs can be bought or sold to meet offset requirements for a facility's expansion in
nonattainment areas.
LAER
Sources that trigger NSR in nonattainment areas must meet a more stringent level of control called Lowest Achievable
Emissions Reductions (LAER). LAER is defined as the most effective control technology demonstrated in practice,
without regard to cost. Like BACT, LAER is a moving target that becomes more stringent over time and must be evaluated
and negotiated on a case-by-case basis.
In both the NSR and PSD programs there is a strong incentive to minimize emissions to stay below the major source
threshold. This can be done through a choice of technology, limits on system size or hours of operation, or voluntary
use of add-on control technology. For example, a voluntary limit on hours of operation would proportionally increase
the size unit that would fit within the major source threshold. A source would need to take an enforceable limit
on operating hours in its permit to qualify. This is known as a "synthetic minor." In some cases, this
may not be consistent with the desired utilization of the equipment and may not be an option for the owner.
| Pollutant |
New Source in a Moderate Nonattainment Area |
New Source in a Serious or Worse Nonattainment Area |
Modified Source |
| Lead |
100 tpy |
100 tpy |
0.6 tpy |
| SO2 |
100 tpy |
100 tpy |
40 tpy |
| NOx |
100 tpy |
100 tpy |
40 tpy |
| PM |
100 tpy |
70 tpy |
14 tpy |
| CO |
100 tpy |
50 tpy |
100 tpy |
Major Source Thresholds for Criteria Pollutants in Nonattainment Areas
(tons per year)
|
Pollutant
|
New Source in a Moderate Nonattainment Area
|
New Source in a Serious or Worse Nonattainment Area
|
Modified Source
|
|
Lead
|
100 tpy
|
100 tpy
|
0.6 tpy
|
|
SO2
|
100 tpy
|
100 tpy
|
40 tpy
|
|
NO2
|
100 tpy
|
100 tpy
|
40 tpy
|
|
PM
|
100 tpy
|
70 tpy
|
14 tpy
|
|
CO
|
100 tpy
|
50 tpy
|
100 tpy
|
Nonattainment Area Maps
The following are nonattainment maps designated by pollutant:
8-hr Ozone
CO
SO2
PM-10
PM-2.5
Lead
Title V
Title V of the 1990 Clean Air Act Amendments requires all major sources and some minor sources of air
pollution to obtain an operating permit. A Title V permit grants a source permission to operate. The permit
includes all air pollution requirements that apply to the source, including emissions limits and monitoring,
record keeping, and reporting requirements. It also requires that the source report its compliance status
with respect to permit conditions to the permitting authority.
A Title V permit is also referred to as a federal operating permit.
Part 70 is the section in the Code of Federal Regulations where Title V is detailed. "Title V Permit" and
"Part 70 Permit" are used interchangeably.
Title V is largely an administrative program
designed to ensure that the requirements of other regulatory programs are met. This program is different from the
state pre-construction permitting program, which sets emission control and compliance requirements. The operating
permit program is a federal program administered by the states, but it does not set its own compliance requirements.
A facility needs a Title V Permit if its potential to emit (PTE) air pollutants when it is operating at its maximum capacity
is over the below thresholds:
| Pollutant |
PTE Tons per Year |
| VOC |
100 |
| CO |
100 |
| NOx |
100 |
| SO2 |
100 |
| PM-10 |
100 |
| Individual Hazardous Air Pollutants (HAPs) |
10 |
| Combined HAPs |
25 |
| Lead |
10 |
The primary concern with triggering Title V is the administrative burdens that may be imposed in applying for
and receiving an additional permit and continuing monitoring and reporting requirements. Thresholds for triggering
Title V vary based on the attainment status of the geographic region. Sources that trigger these thresholds are
considered significant sources. In the operating permits program, significant sources include those that have a
potential to emit 100 tons per year of a criteria pollutant. Sources that have the potential to emit lesser amounts
of air pollutants are also included, if they are located in areas not meeting the National Ambient Air Quality
Standards for a particular pollutant. Some states also use the Title V threshold as a trigger for state emission
control requirements. A Title V permit needs to be renewed every five (5) years.
MACT
EPA has recently proposed several new MACT standards, among them are standards for turbines and internal combustion
engines. The new standards would put limits on the amount of emissions that a major source can release and are
aimed at reducing formaldehyde, acrolein, methanol and acetaldehyde emissions. A major source is one that emits
more than 10 tons per year of a single hazardous air pollutant (HAP) or 25 tons per year of a combination of HAPs.
Emission limitations for engines and turbines are listed as formaldehyde and carbon monoxide (CO) limits. The EPA
is suggesting that technologies aimed at reducing CO will concurrently reduce other hazardous pollutants to appropriate
levels. This method is suggested, in part, because measuring hazardous emissions can be problematic and complicated
for many units. The assumption that CO control technology will automatically result in control of other hazardous
emissions is likely to be controversial, particularly among industry representatives. EPA is alternately offering
the option of reducing formaldehyde emissions. The required reductions are listed below.
Internal Combustion Engines
The standards would apply to new, reconstructed and some existing stationary IC engines greater than 500 hp and
located at a major source of air toxins. Emission limits are listed for formaldehyde and carbon monoxide only.
The proposed emission limits are as follows:
MACT Formaldehyde Emission Limits for IC Engines
| Technology |
Maximum Formaldehyde Emissions Level |
Control Technology Limits |
| Spark ignition 4-stroke rich burn |
350 ppb |
NSCR* to a reduction of 75% of formaldehyde or more |
| Spark ignition 2-stroke lean burn |
17 ppm |
CO Catalytic oxidation system to a reduction of 60% of CO or more |
| Spark ignition 4-stroke lean burn |
14 ppm |
CO Catalytic oxidation system to a reduction of 93% of CO or more |
| Compression ignition |
580 ppb |
CO Catalytic oxidation system to a reduction of 70% or CO or more |
*An add-on catalytic NOx control device that, in a two-step reaction, promotes the conversion of excess oxygen,
NOx, CO, VOCs into CO2, nitrogen, and water.
Engines operating for emergencies, limited use or burning landfill or digester gas are exempt from the emission
limits. In addition, existing sources are exempted with the exception of spark ignition 4-stroke rich burn engines,
which will have three years to comply with the new standards. The rule is expected to be finalized sometime in
2003. EPA anticipates that 20,300 new engines will be installed by the end of the fifth year of the program. In
addition, 4,600 existing engines may be subject to the rule. However, EPA estimates that only 40% of new and existing
engines are located at major source of air toxics (and therefore subject to the MACT rule).
Combustion Turbines
The standards would apply to all new stationary combustion turbines at a major source and existing lean premix
combustion turbines at a major source. Existing turbines would have up to three years to comply with the new standards.
Sources may opt to comply with new requirements by installing carbon monoxide catalytic oxidation systems for a
reduction of CO emissions by 95%. Sources may also opt to reduce formaldehyde emissions to 43 ppb. Combustion turbines
that are smaller than 1 MW, burn landfill or digester gas, are considered "limited use" or are used for
emergencies only are exempt from this requirement. The EPA estimates that 160 existing turbines and 155 new turbines
per year (for the following five years) will be subject to the requirements. The EPA plans to finalize the rule
in 2003.
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