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1 Regional NEPA Analysis of NOx Emissions from Potential Oil & Gas Development Scott F. Archer USDI - Bureau of Land Management scott_archer@blm.gov March 11, 2004
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2 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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3 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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4 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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5 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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6 Major Analytical Assumptions Montana 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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10 Major Analytical Assumptions Wyoming 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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11 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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12 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 pads Coal Bed Methane Drill Rig
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13 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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14 MT Emission Inventory Coal Bed Methane Sources
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15 MT Emission Inventory Conventional Oil & Gas Sources
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16 MT/WY Project Emissions
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17 MT/WY New & RFFA Emissions
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18 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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19 MT/WY Receptor Locations
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20 Summary of Major Findings Montana 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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21 Summary of Major Findings Wyoming 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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22 Summary of Major Findings Cumulative Montana, Wyoming and Other New & RFFA - Potential to exceed 24-hr PM 2.5 and PM 10 NAAQS - Potential to exceed 24-hr PM 10 PSD Class II - Potential to exceed 24-hr PM 10 PSD Class I (2 areas) - Potential to exceed Annual NO 2 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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23 What about Ozone?
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26 For More Information Please feel free to contact: 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 Denver, Colorado 80225-0047 USA +1.303.236.6400 scott_archer@blm.gov
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28 Northern San Juan Basin Environmental Impact Statement for Coalbed Methane Development 3/1/2004
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29 Existing Oil and Gas Development in the San Juan Basin
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31 Projected Timeline * … DateAction March 2004 Issue DEIS, 60-day comment period begins May 2004Close comment period September 2004Issue FEIS October 2004Issue ROD Mid-Nov 2004Appeal period closes * Schedule is dependent upon NOA approval and completion of air quality coordination.
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32 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 scott_archer@blm.gov
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