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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
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



2
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




3
NAAQS
          Pollutant           Averaging Time         Primary Standard        Secondary Standard
      Particulate Matter         PM10, 24 hr             150 g/m3                 150 g/m3
                                PM2.5, annual             15 g/m3                  15 g/m3
                                 PM2.5, 24 hr             35 g/m3                  35 g/m3
     Sulfur Dioxide (SO2)          annual            80 g/m3 (0.03 ppm)              ----
                                    24 hr           365 g/m3 (0.14 ppm)              ----
                                     3 hr                   ----             1,300 g/m3 (0.5 ppm)
                                     1 hr               Coming Soon                   --
    Nitrogen Dioxide (NO2)         annual           100 g/m3 (0.053 ppm)     100 g/m3 (0.053 ppm)
                                     1 hr           100 ppb (new std form)
         Ozone (O3)                  8 hr                0.075 ppm                0.075 ppm
    Carbon Monoxide (CO)             8 hr             9 ppm (10 g/m3)                ----
                                     1 hr            35 ppm (40 g/m3)                ----
          Lead (Pb)          3-month rolling avg.        0.15 g/m3                   ----




4
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



5
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


6
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




7
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


8
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)




9
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


10
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.




11
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




12
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




13
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”

14
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


15
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




16
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


17
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




18
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




19
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?



20
Final Project Thoughts
        What happens if actual emissions exceed
         BAE + 40 TPY due to the project?
        Maybe PTE isn’t so bad…




21
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




22
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




23
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

24
PM2.5 NAAQS Considerations
                                                 NAAQS
                                                  Level


                                            35
     PM2.5 24-hour Concentration ( g/m3 )




                                                          7 g/m3 available
                                                            for modeling



                                            28

                                                                                Monitored
                                                                             Background Value




25
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

26
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)


27
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

28
ERC Equivalency Demonstration


        Project Location




              ERC Location




29
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



30
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

31
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)




32
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.)

33
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



34
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



35

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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 2
  • 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 3
  • 4. NAAQS Pollutant Averaging Time Primary Standard Secondary Standard Particulate Matter PM10, 24 hr 150 g/m3 150 g/m3 PM2.5, annual 15 g/m3 15 g/m3 PM2.5, 24 hr 35 g/m3 35 g/m3 Sulfur Dioxide (SO2) annual 80 g/m3 (0.03 ppm) ---- 24 hr 365 g/m3 (0.14 ppm) ---- 3 hr ---- 1,300 g/m3 (0.5 ppm) 1 hr Coming Soon -- Nitrogen Dioxide (NO2) annual 100 g/m3 (0.053 ppm) 100 g/m3 (0.053 ppm) 1 hr 100 ppb (new std form) Ozone (O3) 8 hr 0.075 ppm 0.075 ppm Carbon Monoxide (CO) 8 hr 9 ppm (10 g/m3) ---- 1 hr 35 ppm (40 g/m3) ---- Lead (Pb) 3-month rolling avg. 0.15 g/m3 ---- 4
  • 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 5
  • 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 6
  • 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 7
  • 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 8
  • 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) 9
  • 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 10
  • 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. 11
  • 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 12
  • 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 13
  • 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” 14
  • 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 15
  • 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 16
  • 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 17
  • 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 18
  • 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 19
  • 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? 20
  • 21. Final Project Thoughts  What happens if actual emissions exceed BAE + 40 TPY due to the project?  Maybe PTE isn’t so bad… 21
  • 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 22
  • 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 23
  • 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 24
  • 25. PM2.5 NAAQS Considerations NAAQS Level 35 PM2.5 24-hour Concentration ( g/m3 ) 7 g/m3 available for modeling 28 Monitored Background Value 25
  • 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 26
  • 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) 27
  • 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 28
  • 29. ERC Equivalency Demonstration Project Location ERC Location 29
  • 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 30
  • 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 31
  • 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) 32
  • 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.) 33
  • 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 34
  • 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 35

Hinweis der Redaktion

  1. Example from U.S. EPA about CHA