Unleash Your Potential - Namagunga Girls Coding Club
Continuing Evolution of New Source Review
1. Continuing Evolution of New
Source Review
John Egan and Colin McCall
All4 Inc.
2010 Mid-Atlantic Environmental
and Energy Conference and Trade Show
Camp Hill, PA
April 14, 2010
2. Agenda
Brief major new source review primer
Case study example of current issues:
• Applicability analysis
• Excluded emissions
• Tracking against projections
PM2.5 and GHG meet major NSR
Aggregation and offsets for non-attainment
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3. Major NSR Permits
Major new source review (NSR) is the air
permitting program for major new sources
and major modifications.
Two different Major NSR programs:
• Prevention of Significant Deterioration (PSD) for
sources in NAAQS attainment areas
• Non-attainment New Source Review (NNSR) for
sources in NAAQS non-attainment areas
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5. NSR Major Modifications
In order to trigger a major modification
under PSD or NNSR:
• Facility must be an existing major source and
project must result in a significant emissions
increase, or
• Project must be a major source
Different major source thresholds and
significance levels under PSD and NNSR
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6. NSR Major Modifications
Major modifications under both PSD and
NNSR can include:
• New emissions units
• Physical changes to existing emissions units or to
non-emissions units
• Change in the method of operation of existing
emissions units (e.g., debottlenecking)
• Removal of previous permit restrictions
• Use of fuels or raw materials that the unit could
not previously use
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7. Example – How Major NSR Works
The Project
• Existing combination fuel boiler
Fires primarily wood and coal
• Modification:
Increase steam rate (more power)
Burn more wood (biomass)
Install new over fire air system
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8. Considerations
Use NSR Reform:
• Actual-to-projected actual calculations
For this discussion assume:
• Historic decrease in coal use
• Only five years of historic data available
• No baseline adjustments required
• Located in an attainment area
• Able to avoid PSD for all pollutants
• Focus on SO2 only
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9. SO2 Applicability Analysis
Potential to emit (PTE) rate = 500 TPY (no
change)
Baseline period selected is 2003/2004
Baseline actual emission (BAE) rate = 300 TPY
Projected actual emission (PAE) rate = 325 TPY
• PAE – BAE = 25 TPY
(< 40 TPY PSD significance threshold for SO2)
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10. SO2 Baseline/Future
Baseline and Projected Future Actual SO2 Emissions 2003-2018
500
Potential
to Emit
450
Project Occurs
2008
400
Baseline
+ 40 TPY
350
300
Emissions (TPY)
Baseline
300 TPY
250
200
150
100
50
0
2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014-2018
Baseline Actual Emissions YEAR Projected Actual Emissions
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11. Excluded Emissions
§52.21(b)(41)(ii)(c) states that in
determining PAE the source shall exclude
emissions following the project that the unit
could have accommodated during the
baseline period and that are unrelated to
the project, including demand growth.
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12. Excluded Emissions
For example if PAE is 380 TPY:
PAE – BAE = 380 – 300 = 80 TPY
If boiler operated at a rate that resulted in 30 tons
of SO2 during May 2004, a reasonable argument
may exist that the boiler could have
accommodated 360 TPY during baseline period
(i.e., 30 tons/month x 12 months)
Any increase in SO2 cannot be due to the project
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13. Excluded Emissions
Applicability analysis per §52.21(a)(2) and
§52.21(b)(41)(ii)(c) definition of PAE:
Excluded emissions (EE) = CHA – BAE
360 – 300 = 60 TPY
Project increase = PAE – EE – BAE
380 – 60 – 300 = 20 TPY
Currently a controversial topic with U.S. EPA
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14. Excluded Emissions
Do they matter?
• In first case project increase was less than
significant regardless of CHA emissions
• In second case CHA made project not
significant
• Also if the project involved other units that emit
SO2 they could affect applicability analysis
and/or future reporting
Note that the rule says “shall exclude”
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15. Permit Language
Requirement to monitor, calculate, and record
annual boiler SO2 emission rate for 10 years
following project due to:
• Applicability approach
• Increased steaming capacity
• Reasonable possibility of significant increase per
§52.21(r) due to 25 TPY increase not counting excluded
emissions
Requirement to submit report if annual emissions
exceed BAE by a significant amount and differ
from documented projection
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16. Future Tracked Emissions
2009, 2010, 2011 annual SO2 emission rate
is less than BAE + 40 TPY:
• No report required
In 2011 scarcity of biomass results in
greater coal use and annual emissions
exceed preconstruction projection
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17. Future Tracked Emissions
Projected Actual and Actual SO2 Emissions 2009-2012
500
Potential to
Emit
450
400
Baseline Baseline
+ 40 TPY 300 TPY
350
300
Emissions (TPY)
Projected Actual
250
Actual
200
150
100
50
0
2009 2010 2011 2012
YEAR
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18. Future Tracked Emissions
By 2012 increased coal use results in
annual emissions exceeding both the BAE
+ 40 TPY and preconstruction projection:
• Report required
• Justification that emissions are within the
scope of the project
• Possibly use excludable emissions from
baseline period to support
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19. Other Thoughts
What if in 2012 we decide to fire TDF
instead of more coal?
• Likely considered a modification if not allowed
in permit
• New applicability analysis required
• Baseline may need to change
• CHA emissions may be important
• May not be excludable
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20. More Thoughts
The more complicated the project the greater the
potential for confusion and non-compliance. For
example say the project required wood yard
upgrades and netting for PM10:
• Required to track PM10 for project and could have
units greater than and less than projections and
not need to report
• What happens if one unit included in a multi-unit
project isn’t changed?
• How does the next project get permitted?
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21. Final Project Thoughts
What happens if actual emissions exceed
BAE + 40 TPY due to the project?
Maybe PTE isn’t so bad…
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22. PSD/NNSR for Fine Particulate (PM2.5)
Several unique PSD/NNSR issues:
• Difficulty quantifying emissions
• PSD air quality modeling challenges
• NNSR applicability and offset challenges
Impacts to project viability, schedule, and
design
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23. Quantifying PM2.5 Emissions
PSD/NNSR will require establishing
emission limits with a margin of compliance
Published emission factors not widely
available, particularly for condensables
Vendor emission factors are often lacking
Test methods available but may not be
appropriate in certain instances
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24. PM2.5 PSD Air Quality Modeling
Significant impact levels (SILs) not finalized
NAAQS demonstration will be difficult:
• Adding facility-wide modeled concentrations
to nearby monitored concentrations
• Current background concentrations are
above or near the 24-hour and annual
NAAQS level already
24-hour concentrations could be temporally
paired in certain situations
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25. PM2.5 NAAQS Considerations
NAAQS
Level
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PM2.5 24-hour Concentration ( g/m3 )
7 g/m3 available
for modeling
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Monitored
Background Value
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26. PM2.5 NNSR Applicability Challenges
Pennsylvania specific: 10-year deminimis
aggregation
Projects with minor emission increases
must be summed with other increases and
decreases that occurred with a 10-year
lookback
If a project triggers NNSR
requirements, the clock is “reset” with
respect to aggregation
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27. PM2.5 Deminimis Aggregation Example
Major facility with the following historic permitting
activities:
• New project (2 tpy)
• 2007: New storage pile (1.3 tpy)
• 2005: New boiler (2.4 tpy)
• 2004: Boiler uptime improvement (3.5 tpy)
• 2002: New outdoor vent (0.9 tpy)
Total of 10.1 tpy would need to be offset
Same process applies to SO2 (40 tpy threshold)
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28. PM2.5 Offset Challenges
PM2.5 emission reduction credits (ERCs) are in
short supply
Interpollutant trading will help
ERCs are to be obtained from the same
nonattainment area of the project
location, otherwise air quality modeling is
required
Significant limits on the spatial separation
between the sources generating the PM2.5 ERCs
and the project location
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30. Finding PM2.5 ERCs
Direct PM2.5 ERCs are selling in PA for
between $3,000 – $10,000 per ton with very
limited sales of ERCs from which to judge
Determine the amount of ERCs needed
early in their planning process
Begin looking for available ERCs as soon as
possible
Internal reductions of PM2.5 should be given
serious consideration
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31. New NAAQS Levels
1-Hour NO2 NAAQS: 100 ppb
Extremely stringent for a 1-hour averaging
time standard.
No proposed SIL, awaiting guidance.
Proposed 1-Hour SO2 NAAQS with similar
issues as the NO2 NAAQS
No grandfathering of PSD permit applications
that have not received final approval (even
with draft permits)
Challenge for NAAQS demonstrations that
correspond to Title V renewals
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32. New NAAQS Levels
Any major facility will have difficulty
demonstrating compliance using facility-wide
modeling
Strategic approaches to permitting:
Look for emission reductions where they are
available (to either avoid major source
permitting or to decrease modeled impacts)
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33. GHG Tailoring Rule
“Major Sources” of GHGs
Regulated GHG pollutants
PSD implications and timing
U.S. EPA will begin regulating GHGs for
stationary sources in January 2011
No grandfathering for permit
applications that have not been issued
Addressing GHGs in construction permit
emissions inventories and control
technology requirements (BACT, etc.)
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34. Conclusions
NSR applicability process is still evolving
Implications of new NAAQS are immediate
and far reaching
GHGs can’t be ignored
Environmental considerations will impact
planning and design
Pay attention to these issues and try not to
be surprised
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35. Questions?
John and Colin
All4 Inc.
2393 Kimberton Road
P.O. Box 299
Kimberton, PA 19442
610.933.5246 x14 and x20
www.all4inc.com
jegan@all4inc.com
cmccall@all4inc.com
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