Source Reporting Form | Onshore Production [98.236(aa)(1)] |
Required for Selected Industry Segment | No |
Source Reporting Form | Facility Overview [98.236(aa)(2-11)] |
Required for Selected Industry Segment | Yes |
Source Reporting Form | Natural Gas Pneumatic Devices [98.236(b)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 34.5 |
Total Reported CH4 Emissions (mt CH4) | 1073.25 |
Source Reporting Form | Natural Gas Driven Pneumatic Pumps [98.236(c)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 1.8 |
Total Reported CH4 Emissions (mt CH4) | 55.15 |
Source Reporting Form | Acid Gas Removal Units [98.236(d)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 2266.6 |
Source Reporting Form | Dehydrators [98.236(e)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 8874.8 |
Total Reported CH4 Emissions (mt CH4) | 187.28 |
Total Reported N2O Emissions (mt N2O) | 0.001 |
Source Reporting Form | Well Venting for Liquids Unloading [98.236(f)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Source Reporting Form | Completions and Workovers with Hydraulic Fracturing [98.236(g)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Total Reported N2O Emissions (mt N2O) | 0.000 |
Source Reporting Form | Completions and Workovers without Hydraulic Fracturing [98.236(h)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Total Reported N2O Emissions (mt N2O) | 0.000 |
Source Reporting Form | Blowdown Vent Stacks [98.236(i)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 2.9 |
Total Reported CH4 Emissions (mt CH4) | 128.96 |
Source Reporting Form | Atmospheric Storage Tanks [98.236(j)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 1835.1 |
Total Reported CH4 Emissions (mt CH4) | 6.43 |
Total Reported N2O Emissions (mt N2O) | 0.002 |
Source Reporting Form | Transmission Storage Tanks [98.236(k)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Total Reported N2O Emissions (mt N2O) | 0.000 |
Source Reporting Form | Well Testing [98.236(l)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Total Reported N2O Emissions (mt N2O) | 0.000 |
Source Reporting Form | Associated Gas Venting and Flaring [98.236(m)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Total Reported N2O Emissions (mt N2O) | 0.000 |
Source Reporting Form | Flare Stacks [98.236(n)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 23290.4 |
Total Reported CH4 Emissions (mt CH4) | 72.46 |
Total Reported N2O Emissions (mt N2O) | 0.050 |
Source Reporting Form | Centrifugal Compressors [98.236(o)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 250.9 |
Total Reported CH4 Emissions (mt CH4) | 2073.60 |
Source Reporting Form | Reciprocating Compressors [98.236(p)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 1.7 |
Total Reported CH4 Emissions (mt CH4) | 11.10 |
Source Reporting Form | Equipment Leaks Surveys and Population Counts [98.236(q,r)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 38.3 |
Total Reported CH4 Emissions (mt CH4) | 1191.02 |
Source Reporting Form | Offshore Petroleum and Natural Gas Production [98.236(s)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Total Reported CH4 Emissions (mt CH4) | 0.00 |
Total Reported N2O Emissions (mt N2O) | 0.000 |
Source Reporting Form | Enhanced Oil Recovery Injection Pumps [98.236(w)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Source Reporting Form | Enhanced Oil Recovery Hydrocarbon Liquids [98.236(x)] |
Required for Selected Industry Segment | No |
Total Reported CO2 Emissions (mt CO2) | 0.0 |
Source Reporting Form | Combustion Equipment at Onshore Petroleum and Natural Gas Production Facilities, Onshore Petroleum and Natural Gas Gathering and Boosting Facilities, and Natural gas Distribution Facilities [98.236(z)] |
Required for Selected Industry Segment | Yes |
Total Reported CO2 Emissions (mt CO2) | 338569.9 |
Total Reported CH4 Emissions (mt CH4) | 6.38 |
Total Reported N2O Emissions (mt N2O) | 0.638 |
Unit ID or Name [98.236(e)(1)(i)] | Alderman Dehy |
County and State [98.236(e)(1)(xviii)] | LA SALLE, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 10 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 99.32 |
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)] | 7.5 |
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)] | 90 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 355 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0199187 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.838962 |
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)] | 720.7667331 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 7.379668 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0001285 |
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)] | Area 41 Facility (CGP) |
County and State [98.236(e)(1)(xviii)] | LIVE OAK, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 10.9 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 52.92 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Air pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 14 |
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)] | 97 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 1025 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0009934 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.752712 |
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)] | 166.1790052 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.1217842 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000157 |
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)] | Big Wells Compressor Station |
County and State [98.236(e)(1)(xviii)] | Dimmit, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 184.23 |
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)] | 0.3 |
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)] | No |
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)] | 475 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0096069 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.7602685 |
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)] | No |
Were any dehydrator emissions vented to the atmosphere without being routed to a flare or regenerator firebox/fire tubes? [98.236(e)(1)(xvii)] | Yes |
CO2 Emissions from Venting (mt CO2) [98.236(e)(1)(xvii)(A)] | 0.4821066 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 105.1868962 |
Unit ID or Name [98.236(e)(1)(i)] | CGP 31 Dehy |
County and State [98.236(e)(1)(xviii)] | LIVE OAK, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 10 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 97.08 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Electric/Pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 18 |
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)] | 8770 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 89 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 350 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.9686137 |
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)] | 207.7671583 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 2.7206923 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000411 |
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)] | CGP 52 Dehy |
County and State [98.236(e)(1)(xviii)] | BEE, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 82.5 |
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)] | Electric/Pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 10 |
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)] | 8632.32 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 80 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 305 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00498 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.86418 |
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)] | 149.4331821 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.1039392 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000143 |
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)] | CGP 61 Dehy |
County and State [98.236(e)(1)(xviii)] | KARNES, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 32.13 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.8 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Air pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 10 |
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)] | 8739 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 76 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 840 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00341 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.85778 |
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)] | 64.6252653 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0759244 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000067 |
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)] | CGP 81 Dehy |
County and State [98.236(e)(1)(xviii)] | DE WITT, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 55.29 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.8 |
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)] | 3.3 |
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)] | 8763.5 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 98 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 1010 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0232516 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.8204838 |
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)] | 39.0303355 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0303442 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000042 |
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)] | Delmita Station |
County and State [98.236(e)(1)(xviii)] | Starr, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 28.94 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 40 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.74 |
Glycol dehydrator absorbent circulation pump type [98.236(e)(1)(v)] | Electric/Pneumatic |
Dehydrator absorbent circulation rate (gallons per minute) [98.236(e)(1)(vi)] | 6.84 |
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)] | 8736 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 100 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 942.7 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00162 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.86807 |
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)] | 629.5763105 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 1.9881917 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000932 |
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)] | J Lease Compressor Station |
County and State [98.236(e)(1)(xviii)] | Kenedy, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 6 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 320.59 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 4.8 |
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)] | 0.701 |
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)] | 89 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 88 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00649 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.90375 |
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)] | 2.6240638 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0034403 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000003 |
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)] | East Yard Dehy 1 |
County and State [98.236(e)(1)(xviii)] | WEBB, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 30 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 63.33 |
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)] | 7.5 |
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)] | 100 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 900 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0100502 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.8365438 |
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)] | 1687.2054175 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 18.3166883 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0003046 |
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)] | East Yard Dehy 2 |
County and State [98.236(e)(1)(xviii)] | WEBB, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 30 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 63.33 |
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)] | 7.5 |
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)] | 100 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 900 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0100502 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.8365438 |
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)] | 1687.2054175 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 18.3166883 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0003046 |
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)] | North Chesterville |
County and State [98.236(e)(1)(xviii)] | COLORADO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 53.1 |
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)] | 0.48 |
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)] | 86 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 660 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.050989 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.854675 |
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)] | 6.3565697 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0017144 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.000001 |
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)] | Webb County Dehy |
County and State [98.236(e)(1)(xviii)] | WEBB, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 22 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 58.9 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 3 |
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)] | 7.5 |
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)] | 8761 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 98 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 914 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0144419 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.9000622 |
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)] | 1555.8791965 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 20.7146138 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0003164 |
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)] | Silsbee Compressor Station |
County and State [98.236(e)(1)(xviii)] | Hardin, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 265.88 |
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 |
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)] | No |
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)] | 72 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 56 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0092 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.8502 |
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)] | 56.8127517 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0303494 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.000053 |
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)] | West Mesa Dehy |
County and State [98.236(e)(1)(xviii)] | WEBB, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 15 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 105.52 |
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)] | 7.5 |
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)] | 100 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 470 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0067641 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.901495 |
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)] | 803.7465376 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 10.2851358 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0001576 |
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 |
County and State [98.236(j)(1)(i)] | LA SALLE, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 68 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 493 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 73.16 |
Count of tanks with flaring emission control measures [98.236(j)(1)(xiv)(A)] | 3 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.372754 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.372754 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.009356 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.009356 |
Annual CO2 emissions from flaring (mt CO2) [98.236(j)(1)(xiv)(B)] | 304.0698421 |
Annual CH4 emissions from flaring (mt CH4) [98.236(j)(1)(xiv)(C)] | 0.2542974 |
Annual N2O emissions from flaring (mt N2O) [98.236(j)(1)(xiv)(D)] | 0.0002879 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 2236.26 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | No |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | Yes |
Count of atmospheric tanks [98.236(j)(1)(x)] | 3 |
County and State [98.236(j)(1)(i)] | BEE, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 56 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 60 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 67.25 |
Count of tanks that control emissions with vapor recovery systems [98.236(j)(1)(xii)(A)] | 8 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.367593 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.367593 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.008672 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.008672 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 5892.6 |
Total CO2 mass that was recovered (mt CO2) [98.236(j)(1)(xii)(B)] | 0.2085193 |
Total CH4 mass that was recovered (mt CH4) [98.236(j)(1)(xii)(C)] | 3.2260176 |
Annual CO2 emissions from tanks with vapor recovery systems (mt CO2) [98.236(j)(1)(xii)(D)] | 0.0109747 |
Annual CH4 emissions from tanks with vapor recovery systems (mt CH4) [98.236(j)(1)(xii)(E)] | 0.1697904 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | Yes |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 8 |
County and State [98.236(j)(1)(i)] | KARNES, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 56 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 60 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 61.95 |
Count of tanks that control emissions with vapor recovery systems [98.236(j)(1)(xii)(A)] | 8 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.430437 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.430437 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.009224 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.009224 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 11064.18 |
Total CO2 mass that was recovered (mt CO2) [98.236(j)(1)(xii)(B)] | 0.4023906 |
Total CH4 mass that was recovered (mt CH4) [98.236(j)(1)(xii)(C)] | 6.2193897 |
Annual CO2 emissions from tanks with vapor recovery systems (mt CO2) [98.236(j)(1)(xii)(D)] | 0.0211785 |
Annual CH4 emissions from tanks with vapor recovery systems (mt CH4) [98.236(j)(1)(xii)(E)] | 0.3273363 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | Yes |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 8 |
County and State [98.236(j)(1)(i)] | DE WITT, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 56 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 60 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 63.95 |
Count of tanks that control emissions with vapor recovery systems [98.236(j)(1)(xii)(A)] | 16 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.430437 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.430437 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.009224 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.009224 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 17604.6 |
Total CO2 mass that was recovered (mt CO2) [98.236(j)(1)(xii)(B)] | 0.6341744 |
Total CH4 mass that was recovered (mt CH4) [98.236(j)(1)(xii)(C)] | 9.7960992 |
Annual CO2 emissions from tanks with vapor recovery systems (mt CO2) [98.236(j)(1)(xii)(D)] | 0.0333776 |
Annual CH4 emissions from tanks with vapor recovery systems (mt CH4) [98.236(j)(1)(xii)(E)] | 0.5155842 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | Yes |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 16 |
County and State [98.236(j)(1)(i)] | DIMMIT, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 66 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 540 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 74.28 |
Count of tanks with flaring emission control measures [98.236(j)(1)(xiv)(A)] | 2 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.377163 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.377163 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.006791 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.006791 |
Annual CO2 emissions from flaring (mt CO2) [98.236(j)(1)(xiv)(B)] | 788.2690956 |
Annual CH4 emissions from flaring (mt CH4) [98.236(j)(1)(xiv)(C)] | 0.5758741 |
Annual N2O emissions from flaring (mt N2O) [98.236(j)(1)(xiv)(D)] | 0.0007106 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 3982.08 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | No |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | Yes |
Count of atmospheric tanks [98.236(j)(1)(x)] | 2 |
County and State [98.236(j)(1)(i)] | WEBB, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77.2857143 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 449.8571429 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 59.5714286 |
Count of tanks with flaring emission control measures [98.236(j)(1)(xiv)(A)] | 14 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 3 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.379449 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.609923 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.005387 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.016164 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.000907 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 0.035373 |
Annual CO2 emissions from flaring (mt CO2) [98.236(j)(1)(xiv)(B)] | 569.8619447 |
Annual CH4 emissions from flaring (mt CH4) [98.236(j)(1)(xiv)(C)] | 1.1561951 |
Annual N2O emissions from flaring (mt N2O) [98.236(j)(1)(xiv)(D)] | 0.0007015 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 48853.68 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | No |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | Yes |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | Yes |
Count of atmospheric tanks [98.236(j)(1)(x)] | 17 |
County and State [98.236(j)(1)(i)] | KENEDY, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 78 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 870 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 60.9 |
Count of tanks with flaring emission control measures [98.236(j)(1)(xiv)(A)] | 2 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.487366 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.487366 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.009529 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.009529 |
Annual CO2 emissions from flaring (mt CO2) [98.236(j)(1)(xiv)(B)] | 81.5329978 |
Annual CH4 emissions from flaring (mt CH4) [98.236(j)(1)(xiv)(C)] | 0.1453909 |
Annual N2O emissions from flaring (mt N2O) [98.236(j)(1)(xiv)(D)] | 0.0000967 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 1379.82 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | No |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | Yes |
Count of atmospheric tanks [98.236(j)(1)(x)] | 2 |
County and State [98.236(j)(1)(i)] | MC MULLEN, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 70 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 780 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 64.95 |
Count of tanks with flaring emission control measures [98.236(j)(1)(xiv)(A)] | 2 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.609923 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.609923 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.007944 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.007944 |
Annual CO2 emissions from flaring (mt CO2) [98.236(j)(1)(xiv)(B)] | 53.0574389 |
Annual CH4 emissions from flaring (mt CH4) [98.236(j)(1)(xiv)(C)] | 0.1335217 |
Annual N2O emissions from flaring (mt N2O) [98.236(j)(1)(xiv)(D)] | 0.0000714 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 1372.5 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | No |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | Yes |
Count of atmospheric tanks [98.236(j)(1)(x)] | 2 |
County and State [98.236(j)(1)(i)] | ZAPATA, TX |
Select Calculation Method Used (Select from list) [98.236(j)(1)(ii)] | Calculation Methodology 1 |
Name of software package used for Calculation Method 1 [98.236(j)(1)(ii)] | E & P Tank |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 60 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 60 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 44 |
Count of tanks with flaring emission control measures [98.236(j)(1)(xiv)(A)] | 2 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.443004 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.443004 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00818 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.00818 |
Annual CO2 emissions from flaring (mt CO2) [98.236(j)(1)(xiv)(B)] | 36.862463 |
Annual CH4 emissions from flaring (mt CH4) [98.236(j)(1)(xiv)(C)] | 0.050784 |
Annual N2O emissions from flaring (mt N2O) [98.236(j)(1)(xiv)(D)] | 0.0000402 |
Total volume of oil sent to tanks from all gas-liquid separators and direct from wells or non-separator equipment (bbl per yr) [98.236(j)(1)(iii)] | 9461.1 |
Were any emissions from atmospheric tanks controlled with vapor recovery systems? [98.236(j)(1)(xii)] | No |
Were any emissions from atmospheric tanks vented directly to the atmosphere? [98.236(j)(1)(xiii)(A)] | No |
Were any emissions from atmospheric tanks vented to flare(s)? [98.236(j)(1)(xiv)] | Yes |
Count of atmospheric tanks [98.236(j)(1)(x)] | 2 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | 402C Compressor Station |
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)] | 1317600 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.901041 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0033153 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 78.0621604 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4558893 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001627 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Alderman Compressor Station |
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)] | 2612508 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.3437521 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0086746 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 17.7656716 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.0905557 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000347 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 31 Facility (CGP) |
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)] | 285396925.4823244 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.3748207 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.607348 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 15004.414975 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 41.0775089 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0352465 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 32 Facility (CGP) |
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)] | 725290 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.797003 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.020594 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 48.19367 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.2219744 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000896 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 41 Facility (CGP) |
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)] | 29744029.1494876 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.307274 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.588742 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 1771.6160007 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 3.5095937 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0036734 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 52 Facility (CGP) |
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)] | 24867189.7295821 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8236862 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.006556 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 1752.5380454 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 7.8653802 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0030711 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 61 Facility (CGP) |
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)] | 4466594.3101341 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.251337 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.704417 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 250.3567053 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4310862 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0005516 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 81 Facility (CGP) |
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)] | 1575656.0859339 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.728737 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.027895 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 124.4483301 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4409237 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001946 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Area 82 Facility (CGP) |
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)] | 1345585.4357785 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.568832 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.033022 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 115.221839 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.2939182 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001662 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Big Wells Compressor Station |
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)] | 6034608 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.2839248 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.005042 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 231.3506965 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.0820617 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000347 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | East Yard Compressor Station |
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)] | 14280513.2865005 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.4979704 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0088078 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 1137.2540564 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 2.1752388 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0013591 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Freer 44 Compressor Station |
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)] | 2027640 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8383523 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0109961 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 69.9742091 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4886441 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001627 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | J Lease Compressor Station |
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)] | 1494744 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.6834909 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0081055 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 40.9902339 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.2469203 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000879 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Pearsall Compressor Station |
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)] | 562176 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.98 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.01 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 28.9849625 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.2115581 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000694 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Silsbee Compressor Station |
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)] | 1317600 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8502 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00922 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 84.0246262 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4301658 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001627 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Station (SAS) 536 |
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)] | 1317600 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.98 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.01 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 67.933506 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4958392 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001627 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Swift Dehy Station |
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)] | 1895880 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8546023 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0112131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 69.9742091 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.4886441 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0001627 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Webb County Dehy & Compressor Station |
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)] | 2620230.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.7837747 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0146432 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 102.7196629 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.607192 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.000217 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | West Mesa Compressor Station |
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)] | 1050420 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.6647704 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0076174 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 12.9230608 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.0760198 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000271 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Zapata Compressor Station |
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)] | 826801.32 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.6813616 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0136648 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 31.8106454 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.1655426 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000619 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | Delmita Station |
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)] | 37231440 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8816962 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0030752 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 2249.809552 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 12.6054986 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0045981 |