Unit ID or Name [98.236(e)(1)(i)] | e. Aline DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 5.90080316 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.01 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 19.007943279696 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.051850616832 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Amorita DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 15.60611988 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 17.987242699296 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.049309019136 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Ashley DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 6.641019986 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 18.887256539424 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.051567280128 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Byron DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 12.76571801 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 18.5045713864704 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0401312710656 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Cherokee DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 7.478043041 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 2664 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 3.050900642736 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.15553327104 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Driftwood DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 10.8325483 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 9.908616784896 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.50584034304 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Mckee DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 3.039182952 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 2688 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 3.161583645696 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.1607897088 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Salt Fork DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 8.544381728 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 18.70257517056 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.05100060672 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. South Cherokee DEHY |
County and State [98.236(e)(1)(xviii)] | ALFALFA, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 13.86176148 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 11.594853648 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.3990325248 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Bond DEHY |
County and State [98.236(e)(1)(xviii)] | DEWEY, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 11.56997645 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 2736 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 3.066149765664 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.15667167744 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Dart DEHY |
County and State [98.236(e)(1)(xviii)] | DEWEY, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 9.478808125 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 19.1820721535424 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0203472857088 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Robinson Dehy |
County and State [98.236(e)(1)(xviii)] | DEWEY, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 13.02493745 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 9.795657636864 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.50164088832 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Carrier DEHY |
County and State [98.236(e)(1)(xviii)] | GARFIELD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 4.259869148 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 19.095658959744 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.05197879296 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Hillsdale DEHY |
County and State [98.236(e)(1)(xviii)] | GARFIELD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 7.949711138 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 18.71837688384 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.05100060672 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Kremlin DEHY |
County and State [98.236(e)(1)(xviii)] | GARFIELD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 4.221551778 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 19.095658959744 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.05197879296 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Waukomis DEHY |
County and State [98.236(e)(1)(xviii)] | GARFIELD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 4.815870922 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.219661035776 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.52133953536 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Cox DEHY |
County and State [98.236(e)(1)(xviii)] | GRADY, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.074735925 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 93 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 0.91 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 85 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 320 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 3.0840411725856 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.127357318656 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Clyde DEHY |
County and State [98.236(e)(1)(xviii)] | GRANT, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 6.50815147 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.1119414032 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.51567280128 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. County Line DEHY |
County and State [98.236(e)(1)(xviii)] | GRANT, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 3.476063852 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 2496 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 5.455821384 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0148502016 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Smith DEHY |
County and State [98.236(e)(1)(xviii)] | GRANT, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 5.761321739 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.17595682352 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.51850616832 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Bouse Junction DEHY |
County and State [98.236(e)(1)(xviii)] | MAJOR, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 6.203128016 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 3024 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 3.4811601552 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.17752670208 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Canton Dehy |
County and State [98.236(e)(1)(xviii)] | MAJOR, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 9.091297123 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 9.960974976384 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.50868214272 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Chaney Dell DEHY |
County and State [98.236(e)(1)(xviii)] | MAJOR, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.102275938 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 5856 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 13.3223708699136 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.014087006208 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Fisher H-2SV DEHY |
County and State [98.236(e)(1)(xviii)] | MAJOR, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 13.29109536 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 9.795657636864 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.50164088832 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Orienta DEHY |
County and State [98.236(e)(1)(xviii)] | MAJOR, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 6.225174807 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.1119414032 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.51567280128 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Anderson Creek DEHY |
County and State [98.236(e)(1)(xviii)] | WOODS, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.385931419 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 2496 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 5.47371287424 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.01493047296 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Liberty DEHY |
County and State [98.236(e)(1)(xviii)] | WOODS, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 7.275440348 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.04801839056 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.51283943424 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Megan DEHY |
County and State [98.236(e)(1)(xviii)] | WOODS, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 7.136026853 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.0563812856 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.51283943424 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. North Alva DEHY |
County and State [98.236(e)(1)(xviii)] | WOODS, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 6.072107131 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.1119414032 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.51567280128 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Winchester DEHY |
County and State [98.236(e)(1)(xviii)] | WOODS, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.394709822 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 2496 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 5.47371287424 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.01493047296 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Wolgamott DEHY |
County and State [98.236(e)(1)(xviii)] | WOODS, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 7.130160764 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 18.783480404592 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.051283943424 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Bent Creek DEHY |
County and State [98.236(e)(1)(xviii)] | WOODWARD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.872164131 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 19.295915643072 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.05254377984 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Freedom DEHY |
County and State [98.236(e)(1)(xviii)] | WOODWARD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 3.808317733 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 19.794103927488 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.02090451456 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Quinlan DEHY |
County and State [98.236(e)(1)(xviii)] | WOODWARD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 5.935000712 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 18.991032674256 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.051850616832 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00000 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unit ID or Name [98.236(e)(1)(i)] | e. Walker DEHY |
County and State [98.236(e)(1)(xviii)] | WOODWARD, OK |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 3.256490102 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 106.04 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 7 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Natural gas pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 3.5 |
Report type of absorbent used [98.236(e)(1)(vii)] | Triethylene glycol (TEG) |
Report whether stripper gas is used in glycol dehydrator [98.236(e)(1)(viii)] | No |
Report whether a flash tank separator is used in glycol dehydrator [98.236(e)(1)(ix)] | Yes |
Total time the glycol dehydrator is operating (hours) [98.236(e)(1)(x)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 120 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 950 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.004 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.841 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | No |
Were any dehydrator emissions vented to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvi)] | Yes |
CO2 Emissions from Flares or Regenerators (mt CO2) [98.236(e)(1)(xvi)(A)] | 10.27605744288 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.522612864 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.00001 |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | No |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | n. Chaney Dell 10 Flare |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | Yes |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 112000 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.841 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.004 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 6.92274912 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.036169728 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.00001 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Aline DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 160747.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0431 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Amorita DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 151963.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.338 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0425 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Ashley DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 159868.8 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Byron DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 154598.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.96 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.338 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0426 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Cherokee DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 48218.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0429 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Driftwood DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 156355.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.337 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0428 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Mckee DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 49996.8 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Salt Fork DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 158112 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0429 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. South Cherokee DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 153720 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.6 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.338 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0426 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Bond DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 48427.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.337 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0427 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Dart DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 157233.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.337 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0428 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Robinson Dehy |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 154598.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.338 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0426 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Carrier DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 161625.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0431 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Hillsdale DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 158112 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0429 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Kremlin DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 161625.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0431 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Waukomis DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 161625.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0431 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Cox DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 45588.96 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.291 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0381 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Clyde DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 159868.8 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. County Line DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 46176 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Smith DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 160747.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Bouse Junction DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 55036.8 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Canton Dehy |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 157233.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.337 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0429 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Chaney Dell DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 109507.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Fisher H-2SV DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 154598.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.338 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0426 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Orienta DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 159868.8 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Anderson Creek DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 46425.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Liberty DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 158990.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Megan DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 158990.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. North Alva DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 159868.8 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Winchester DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 46425.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Wolgamott DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 158990.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Bent Creek DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 163382.4 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Freedom DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 162504 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0431 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Quinlan DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 160747.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.95 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.336 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.043 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | e. Walker DEHY |
Does the flare stack have a continuous flow monitor on gas to the flare? [98.236(n)(2)] | No |
Does the flare stack have a continuous gas analyzer on gas to the flare? [98.236(n)(3)] | No |
Were CEMS used to measure CO2 emissions for the flare stack? [98.233(n)(8)] [98.236(n)(12)] | No |
Volume of gas sent to flare, Vs (standard cubic feet) [98.236(n)(4)] | 162504 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.5 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.335 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 0 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Valve |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 20 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 1045.25 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0.0215522188 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 1.6540303584 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Flange |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 1 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 2061 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0.00177790104 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0.13644545472 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Connector (other) |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 93 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 1028.39784946237 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0.02615972632 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 2.00763466176 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Open-Ended Line |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 9 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 386.333333333333 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0.00204837024 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0.15720268032 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Pressure Relief Valve |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Pump Seal |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 16 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 1384.875 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0.01724955984 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 1.32382173312 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Gas Service - Other |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 1 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 1872 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0.0017724096 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0.1360240128 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Valve |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Flange |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Connector (other) |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Open-Ended Line |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Pump |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Agitator Seal |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Light Crude Service - Other |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Valve |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Flange |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Connector (other) |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Open-Ended Line |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Pump |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Agitator Seal |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Component Type [98.236(q)(2)(i)] | Onshore Production or GB Components, Heavy Crude Service - Other |
Total number of surveyed component type identified as leaking, xp [98.236(q)(2)(ii)] | 0 |
Average time the surveyed components are assumed to be leaking and operational, Tp,z (hours) [98.236(q)(2)(iii)] | 0 |
CO2 Emissions (surveyed components identified as leaking only) (mt CO2) [98.236(q)(2)(iv)] | 0 |
CH4 Emissions (surveyed components identified as leaking only) (mt CH4) [98.236(q)(2)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gas Service - Valves |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 65348 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 14.6191065987226 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 1121.52051535012 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gas Service - Connectors |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 230797 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 7.25407836547968 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 556.504438346035 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gas Service - Open ended lines |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 4609 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0.26416274214528 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 20.2655294088192 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gas Service - Pressure relief valves |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 4563 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 1.62821195791488 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 124.910034810163 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Light crude service - Valves |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Light crude service - Flanges |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Light crude service - Connectors |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Light crude service - Open ended lines |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Light crude service - Pumps |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Light crude service - Other equipment leak sources (such as instruments, loading arms, stuffing boxes, compressor seals, dump lever arms, breather caps) |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Heavy crude service - Valves |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Heavy crude service - Flanges |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Heavy crude service - Connectors |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Heavy crude service - Open ended lines |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Heavy crude service - Other equipment leak sources (such as instruments, loading arms, stuffing boxes, compressor seals, dump lever arms, breather caps) |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gathering pipelines - Protected steel gathering pipeline |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 3581 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 3.10207304928 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 238.06936283904 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gathering pipelines - Unprotected steel gathering pipeline |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 61 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 1.86520281696 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 143.14545116928 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gathering pipelines - Plastic/composite gathering pipeline |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 2605 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 12.0032148 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 921.1896864 |
Emission Source Type (Eq. W-32A) [98.232(c)(21)] [98.233(r)] | Gathering pipelines - Cast iron gathering pipeline |
Geographic Location (according to Table W-1D) [98.236(r)(1)(i)] | Western U.S. |
Total number of emission source type, Counte (for gathering pipelines, this value is the number of miles of pipeline per material type) [98.236(r)(1)(ii)] | 0 |
Average estimated time that the emission source type was operational in the calendar year, Te (hours) [98.236(r)(1)(iii)] | 8760 |
CO2 Emissions (mt CO2) [98.236(r)(1)(iv)] | 0 |
CH4 Emissions (mt CH4) [98.236(r)(1)(v)] | 0 |