Regional NEPA Analysis of NOx Emissions from Potential Oil & Gas Development
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Regional NEPA Analysis of NOx Emissions
from Potential Oil & Gas Development
Scott F. Archer
USDI - Bureau of Land Management
March 11, 2004
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This presentation describes the Montana and Wyoming Powder River Basin Oil & Gas Air Quality Impact Assessments’:
• Major Analytical Assumptions• Major Emission Sources• Analysis Methodology• Summary of Major Findings• Technical Support Document
Outline
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NEPA Air Quality Impact Analyses
• Key issues: Potential impacts to Standards, Increments, HAPs, visibility, atmospheric deposition
• Thresholds: Legal limits or “best science”• Analysis and disclosure process (not decision)• Focus on greatest potential impacts
• Affected Environment = Background• Reasonably Foreseeable Future Activities• No Action = Background + RFFA• Potential Direct impacts = “Alternative”• Potential Cumulative = No Action + “Alternative”
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History• WY PRBO&G Project Air Quality Analysis began
in June 2000• Wyodak EIS was just completed• DM&E Railroad Expansion was underway• MT PRBO&G Project Air Quality Analysis began
in April 2001• For a variety of reasons, both the MT and WY
PRBO&G DEIS’ were delayed until January 2002
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History• Initial combined Air Quality modeling results
became available in April 2002• May 2002 Comments on both DEIS’• The emissions inventory was updated through
May 31, 2002• Significant re-modeling completed December
2002• Both the MT and WY PRBO&G FEIS’ were
published January 2003
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Major Analytical AssumptionsMontana and Wyoming
Study Area - New 5 State Domain
(2.2 times larger than DM&E)
Regional Meteorology - 1996 MM5 (36km)
CALMET Grid size - 4km
CALPUFF Receptor Grid
near-field: 0.1 and 1km
far-field: 1km, + lakes
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Major Analytical AssumptionsWyoming Montana
Max, 50-100% electric, “NA” Max, electric booster,“NA”
~40,000 new CBM wells ~26,000 new CBM wells
~1,000 “booster” comps ~1,000 “field” comps
~300 “recip” comps ~100 “sales” comps
~ 3,000 conventional ~2,500 conventional
10 year “LOP” 20 year “LOP”
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Major Emission Sources
• Construction Activities– Road and pad clearing– Rig up and drilling– Rig down and testing
• Operation Activities– 25 wells per field/booster compressor – 250 wells per sales/reciprocating compressor
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Construction Activities• Access road and well
pad construction
(3 days)
• Rig-up and drilling (4 days)
• Rig-down and testing (5 days, including 1 day flaring)
• Compressor padsCoal Bed Methane Drill Rig
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Operating Emissions• Up to eight well pads
per square mile, three wells per pad
• 90% of wells drilled assumed to produce
• Average 200 Mcf/day production over 10 - 20 year “life of project”
Two 380 horsepower, CBM-fired
reciprocal field compressors
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MT Emission InventoryCoal Bed Methane Sources
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MT Emission InventoryConventional Oil & Gas Sources
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MT/WY Project Emissions
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MT/WY New & RFFA Emissions
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Analysis Methodology• MM5/CALMET and CALPUFF Models• Both near- and far-field analyses• Maximum HAP, incremental MLE and MEI cancer
risks based on a “reasonable, but conservative” well pad and compressor scenario
• Range of temporary generator impacts for power and pumping
• Post-processing for Atmospheric Deposition (USDA-FS protocol) and Regional Haze (FLAG protocol)
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MT/WY Receptor Locations
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Summary of Major FindingsMontana FEIS (Alt E - Preferred)
- Comply with State/National Standards- Comply with PSD Class I and II Increments- Above lowest State’s 8-hr formaldehyde AACL; well within range- Within incremental cancer risk thresholds- Within Atmos. Deposition/ANC thresholds- Exceed 1.0 dv “just noticeable change” at seven mandatory federal PSD Class I Areas for 0 to 3 days per year (not likely to actually occur)
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Summary of Major FindingsWyoming FEIS (Alt 2A - Preferred)
- Comply with State/National Standards- Comply with PSD Class I and II Increments- Above lowest State’s 8-hr formaldehyde AACL; well within range- Within incremental cancer risk thresholds- Within Atmos. Deposition/ANC thresholds- Exceed 1.0 dv “just noticeable change” at ten mandatory federal PSD Class I Areas for 0 to 4 days per year (not likely to actually occur)
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Summary of Major FindingsCumulative Montana, Wyoming and Other New & RFFA
- Potential to exceed 24-hr PM2.5 and PM10 NAAQS
- Potential to exceed 24-hr PM10 PSD Class II
- Potential to exceed 24-hr PM10 PSD Class I (2 areas)
- Potential to exceed Annual NO2 PSD Class I- Potential to exceed ANC thresholds (2 lakes)- Exceed 1.0 dv “just noticeable change” at all fourteen mandatory federal PSD Class I Areas for 2 to 32 days per year
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What about Ozone?
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For More Information
Please feel free to contact:Scott F. Archer
Senior Air Resource SpecialistUSDI – Bureau of Land ManagementNational Science and Technology CenterDenver Federal Center, Building 50P.O. Box 25047Denver, Colorado [email protected]
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Northern San Juan Basin Environmental Impact Statement for Coalbed Methane Development
3/1/2004
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Existing Oil and Gas
Development in the San Juan
Basin
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Projected Timeline * …
Date Action
March 2004 Issue DEIS, 60-day comment period begins
May 2004 Close comment period
September 2004
Issue FEIS
October 2004 Issue ROD
Mid-Nov 2004 Appeal period closes
* Schedule is dependent upon NOA approval and completion of air quality coordination.
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For More Information
Scott F. Archer
Senior Air Resource Specialist
USDI-Bureau of Land Management
National Science and Technology Center
Denver Federal Center, Building 50
P.O. Box 25047, ST-133
Denver, Colorado 80225-0047
303.236.6400
303.236.3508 Fax
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