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Potential PM2.5 and CPM Pitfalls in
Permitting, Testing and Compliance
NCASI Southern Regional Meeting
June 10, 2014
Glenn Rives, International Paper
John Egan, All4 Inc.
Agenda
• Project overview
• PSD applicability assessment
• Permitting strategy
• PM2.5 and CPM baseline data
• Compliance testing results
• Critical review and planning
• Outcome and learnings
Project Overview
• Bleached and unbleached Kraft Mill
• Modifications to pulp lines
• Production increase
• Debottlenecked recovery operations
PSD Applicability
• Actual-to-projected actual assessment
• No contemporaneous projects
• Decreases in some pollutants due to project
• No project netting
Project Emissions Baseline Data
• Baseline data from reported emissions
• Missing data for PM2.5 and CPM
• Test data and NCASI factors
• Projected actuals conservatively estimated
Project Emissions Increases
• PSD applicability Step 1 – project increases
• Project increases alone PSD significant for:
• VOC, NOX, PM, PM10, PM2.5
• Biogenic deferral for CO2e
VOC NOX PM PM10 PM2.5
Step 1
Total Project-Related Emissions Increases 48 193 93 82 65
PSD Significance Levels 40 40 25 15 10
Step 1 - Project Increases Exceed PSD Significance
Levels?
Yes Yes Yes Yes Yes
Permitting Strategy and Boiler MACT
• Coal boiler conversion to natural gas option
• Emission reductions available for netting
• Other project reductions made federally
enforceable
• Net decreases less than PSD significant
• Construction permit issued with testing
requirements including PM2.5
Summary of Project Emissions
VOC NOX PM PM10 PM2.5
Step 1
Total Project-Related Emissions Increases 48 193 93 82 65
PSD Significance Levels 40 40 25 15 10
Step 1 - Project Increases Exceed PSD Significance Levels? Yes Yes Yes Yes Yes
Step 2
Emission Increases During the Contemporaneous Period 7 - - - -
Emission Decreases During the Contemporaneous Period 17 183 81 71 56
Total Net Emissions Increase 38 10 12 11 9
PSD Significance Levels 40 40 25 15 10
Step 2 - Net Increases Exceed PSD Significance Levels? No No No No No
Criticality of PM10/PM2.5 Emission
Data
• Recovery area sources largest contributors to
increases
• Concern with lack of data therefore pre-project
testing
• Results compared with other IP and NCASI data
• Projected actual emissions set conservatively
with margins added
CPM Emission Factor Evaluation
(Pre-project)
0
0.1
0.2
0.3
0.4
0.5
Avg 4 tests
(2 per RB)
NCASI
5 RBs (Avg)*
Other IP Sites
7 RBs (Avg)*
Permit Basis
CPMlb/TBLS(virgin)
* Emissions Adjusted to virgin TBLS based on 1.2 TBLS as fired/(TBLS virgin)
Selected factor with safety
margin to assure confident
Non-PSD permit decision
CPM Stack Test Demonstration
(Post-project)
1.15 lb CPM/TBLS-virgin
4 times higher than
expected
Mostly organic > 80 wt%
~ 195 ppmdv as carbon
or
~ 53 ppmdv as propane
0.00
0.20
0.40
0.60
0.80
1.00
1.20
Permit Basis Post-project test
CPMlb/TBLS(virgin)
?
Critical Assessment
Systematic Review - Possible Explanations
• Changes in Operating Conditions?
• Physical or Chemical Changes?
• Sample Collection/Analysis?
• True Emissions Variability?
Assessment Findings
• Process Review
• Similar process & operating conditions all test
programs
• No physical/operational changes
• Previous Stack Test Programs
• CPM coupled with M201A trains
• Test plans/equipment selected to satisfy M201A
cyclone cut point constraints
• Insufficient sample volumes/collected mass for CPM
• No Train/Field Reagent Blanks
Re-test Planning-1
• Use CEMs to confirm exhaust gas levels of CO and
total hydrocarbons are within expected ranges
• Extend CEMs monitoring over several days to
characterize typical values and ranges
• Collect and analyze Liquor and Smelt Chemical
Composition, HHV
Re-test Planning-2
• Reduce sampling equipment/reagent residues
• Confirm Field/Lab Glassware & Reagent purity in advance
• 4 Sampling Train Recovery Blanks
• Increase measurement certainty by:
• Increasing sample volumes (> 75 cubic ft/run)
• Targeting > 50 mg CPM
• Tightening constant weight criteria to +/- 0.2 mg
• Using only glass or Teflon® weighing containers
Re-test Results
Two 3-run series each RB
Average CPM = 0.05 lb/TBLS
virgin
In Expected Range
Predominately inorganic CPM
0
0.1
0.2
0.3
0.4
0.5
Avg 4
tests
(2 per RB)
NCASI
5 RBs
(Avg)*
Other IP
Sites
7 RBs
(Avg)*
Permit
Basis
Re-Test
Avg 12
runs (6 per
RB)
CPMlb/TBLS(virgin)
Re-test CPM Results
Conclusions and Takeaways
• CPM and lower PM2.5 permitting thresholds bring
scrutiny to very small “projects”
• Don’t wait till you have a “project” to test CPM
• Develop a site-specific CPM and PM2.5 emission
“history”
• Don’t over complicate the test constraints – decouple
M201 and M202
• Rely on literature emission factors to put you in the
ballpark – don’t count on for “compliance”
• Design and execute test programs to answer critical
questions at appropriate certainty level
• Don’t set yourself up for surprises

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Potential PM2.5 and CPM Pitfalls in Permitting, Testing, and Compliance

  • 1. Potential PM2.5 and CPM Pitfalls in Permitting, Testing and Compliance NCASI Southern Regional Meeting June 10, 2014 Glenn Rives, International Paper John Egan, All4 Inc.
  • 2. Agenda • Project overview • PSD applicability assessment • Permitting strategy • PM2.5 and CPM baseline data • Compliance testing results • Critical review and planning • Outcome and learnings
  • 3. Project Overview • Bleached and unbleached Kraft Mill • Modifications to pulp lines • Production increase • Debottlenecked recovery operations
  • 4. PSD Applicability • Actual-to-projected actual assessment • No contemporaneous projects • Decreases in some pollutants due to project • No project netting
  • 5. Project Emissions Baseline Data • Baseline data from reported emissions • Missing data for PM2.5 and CPM • Test data and NCASI factors • Projected actuals conservatively estimated
  • 6. Project Emissions Increases • PSD applicability Step 1 – project increases • Project increases alone PSD significant for: • VOC, NOX, PM, PM10, PM2.5 • Biogenic deferral for CO2e VOC NOX PM PM10 PM2.5 Step 1 Total Project-Related Emissions Increases 48 193 93 82 65 PSD Significance Levels 40 40 25 15 10 Step 1 - Project Increases Exceed PSD Significance Levels? Yes Yes Yes Yes Yes
  • 7. Permitting Strategy and Boiler MACT • Coal boiler conversion to natural gas option • Emission reductions available for netting • Other project reductions made federally enforceable • Net decreases less than PSD significant • Construction permit issued with testing requirements including PM2.5
  • 8. Summary of Project Emissions VOC NOX PM PM10 PM2.5 Step 1 Total Project-Related Emissions Increases 48 193 93 82 65 PSD Significance Levels 40 40 25 15 10 Step 1 - Project Increases Exceed PSD Significance Levels? Yes Yes Yes Yes Yes Step 2 Emission Increases During the Contemporaneous Period 7 - - - - Emission Decreases During the Contemporaneous Period 17 183 81 71 56 Total Net Emissions Increase 38 10 12 11 9 PSD Significance Levels 40 40 25 15 10 Step 2 - Net Increases Exceed PSD Significance Levels? No No No No No
  • 9. Criticality of PM10/PM2.5 Emission Data • Recovery area sources largest contributors to increases • Concern with lack of data therefore pre-project testing • Results compared with other IP and NCASI data • Projected actual emissions set conservatively with margins added
  • 10. CPM Emission Factor Evaluation (Pre-project) 0 0.1 0.2 0.3 0.4 0.5 Avg 4 tests (2 per RB) NCASI 5 RBs (Avg)* Other IP Sites 7 RBs (Avg)* Permit Basis CPMlb/TBLS(virgin) * Emissions Adjusted to virgin TBLS based on 1.2 TBLS as fired/(TBLS virgin) Selected factor with safety margin to assure confident Non-PSD permit decision
  • 11. CPM Stack Test Demonstration (Post-project) 1.15 lb CPM/TBLS-virgin 4 times higher than expected Mostly organic > 80 wt% ~ 195 ppmdv as carbon or ~ 53 ppmdv as propane 0.00 0.20 0.40 0.60 0.80 1.00 1.20 Permit Basis Post-project test CPMlb/TBLS(virgin) ?
  • 12. Critical Assessment Systematic Review - Possible Explanations • Changes in Operating Conditions? • Physical or Chemical Changes? • Sample Collection/Analysis? • True Emissions Variability?
  • 13. Assessment Findings • Process Review • Similar process & operating conditions all test programs • No physical/operational changes • Previous Stack Test Programs • CPM coupled with M201A trains • Test plans/equipment selected to satisfy M201A cyclone cut point constraints • Insufficient sample volumes/collected mass for CPM • No Train/Field Reagent Blanks
  • 14. Re-test Planning-1 • Use CEMs to confirm exhaust gas levels of CO and total hydrocarbons are within expected ranges • Extend CEMs monitoring over several days to characterize typical values and ranges • Collect and analyze Liquor and Smelt Chemical Composition, HHV
  • 15. Re-test Planning-2 • Reduce sampling equipment/reagent residues • Confirm Field/Lab Glassware & Reagent purity in advance • 4 Sampling Train Recovery Blanks • Increase measurement certainty by: • Increasing sample volumes (> 75 cubic ft/run) • Targeting > 50 mg CPM • Tightening constant weight criteria to +/- 0.2 mg • Using only glass or Teflon® weighing containers
  • 16. Re-test Results Two 3-run series each RB Average CPM = 0.05 lb/TBLS virgin In Expected Range Predominately inorganic CPM 0 0.1 0.2 0.3 0.4 0.5 Avg 4 tests (2 per RB) NCASI 5 RBs (Avg)* Other IP Sites 7 RBs (Avg)* Permit Basis Re-Test Avg 12 runs (6 per RB) CPMlb/TBLS(virgin) Re-test CPM Results
  • 17. Conclusions and Takeaways • CPM and lower PM2.5 permitting thresholds bring scrutiny to very small “projects” • Don’t wait till you have a “project” to test CPM • Develop a site-specific CPM and PM2.5 emission “history” • Don’t over complicate the test constraints – decouple M201 and M202 • Rely on literature emission factors to put you in the ballpark – don’t count on for “compliance” • Design and execute test programs to answer critical questions at appropriate certainty level • Don’t set yourself up for surprises