Unit ID or Name [98.236(e)(1)(i)] | TX DEHY1 |
County and State [98.236(e)(1)(xviii)] | GALVESTON, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.45 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 33.26 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.18 |
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)] | 0.1 |
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)] | 65 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 500 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01277 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.90472 |
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)] | 0.4824882 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 4.0361566 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY2 |
County and State [98.236(e)(1)(xviii)] | ORANGE, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.6 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 24.05 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 0.75 |
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)] | 1.1 |
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)] | 61 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 636 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00272 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.87379 |
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)] | 210.4237551 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.8998841 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0003591 |
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)] | 0.1265981 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.3673815 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY3 |
County and State [98.236(e)(1)(xviii)] | FORT BEND, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 9.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 47.76 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.54 |
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)] | 1.86 |
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)] | 720 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00799 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.84296 |
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)] | 0.9201218 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 1.0581951 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY4 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.6 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 54.28 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.66 |
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)] | 0.1 |
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)] | 90 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 740 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 0.8501876 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 6.1002055 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY5 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.9 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 27.26 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 0.86 |
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)] | 1.3 |
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)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 75 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 1012 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 0.8205201 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.5617184 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY6 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.9 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 99.76 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 3.87 |
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)] | 1.1 |
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)] | 1020 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 235.1292831 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 1.327419 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0005131 |
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)] | TX DEHY7 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.9 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 39.09 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.27 |
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)] | 1.1 |
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)] | 80 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 760 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 2.5851597 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0066821 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000043 |
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)] | TX DEHY8 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.978 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 36.35 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.18 |
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)] | 1.1 |
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)] | 78 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 770 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 7.928371 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 54.3542204 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY9 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.978 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 36.35 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.18 |
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)] | 1.1 |
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)] | 78 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 770 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 7.928371 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 54.3542204 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY10 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 0.99 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 45.66 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.54 |
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)] | 1.1 |
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)] | 88 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 860 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 8.2353909 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 59.6873947 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY11 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 25.99 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 0.81 |
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)] | 1.3 |
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)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 69 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 820 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 0.7738034 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.4583578 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY12 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.13 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 27.84 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.34 |
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)] | 0.5 |
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)] | 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)] | 70 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 780 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 3.5292341 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 24.37404 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY13 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.2 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 29.99 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.04 |
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)] | 0.5 |
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)] | 72 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 770 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 0.1719892 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.1193758 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY14 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.2 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 39.88 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.32 |
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)] | 1.1 |
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)] | 80 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 740 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 7.6093104 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 51.933594 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY15 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.3 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 56.6 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.98 |
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)] | 1.1 |
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)] | 600 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | Yes |
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)] | 3.4458271 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0077128 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000056 |
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)] | TX DEHY16 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, 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)] | 38.7 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.28 |
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)] | 1.1 |
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)] | 74 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 600 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 175.1305109 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.8468529 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0003439 |
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)] | TX DEHY17 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.8 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 39.72 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.32 |
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)] | 1.3 |
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)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 75 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 605 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 0 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0 |
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)] | 0.8561479 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.5606458 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY18 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.84 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 31.14 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.02 |
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)] | 1.3 |
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)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 75 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 835 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 10.4227731 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 71.8991982 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY19 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.84 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 31.14 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.02 |
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)] | 1.3 |
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)] | 8784 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 75 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 835 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 10.4227731 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 71.8991982 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY20 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 1.85 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 46.61 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.01 |
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)] | 0.5 |
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)] | 80 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 605 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 0.2656628 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.1890767 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY21 |
County and State [98.236(e)(1)(xviii)] | HIDALGO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.1 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.12 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.37 |
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)] | 1.3 |
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)] | 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)] | 1089 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00131 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.92197 |
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)] | 0.0854771 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.7656837 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY22 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.6 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 45.82 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.71 |
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)] | 1.1 |
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)] | 82 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 670 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.001849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 6.9236454 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 46.992809 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY23 |
County and State [98.236(e)(1)(xviii)] | HIDALGO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.8 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 43.27 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.41 |
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)] | 1.3 |
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)] | 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)] | 1010 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00131 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.92197 |
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)] | 0.0853847 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 0.7152835 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY24 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.9 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 44.79 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.72 |
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)] | 1.1 |
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)] | 780 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 7.7612748 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 54.748443 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY25 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 3.854 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 28.4 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 0.95 |
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)] | 1.8 |
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)] | 72 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 830 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 14.0928735 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 96.1883586 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY26 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 3.854 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 28.4 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 0.95 |
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)] | 1.8 |
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)] | 72 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 830 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 14.0928735 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 96.1883586 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY27 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 4.7 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
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)] | 1.1 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 1.2720304 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0059004 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000025 |
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)] | TX DEHY28 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 4.722 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
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)] | 1.1 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 1.2720304 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0059004 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000025 |
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)] | TX DEHY29 |
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)] | 5.6 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 25.36 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 0.82 |
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)] | 2.8 |
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)] | 65 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 710 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.0209 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.91683 |
Were any dehydrator emissions vented to a vapor recovery device? [98.236(e)(1)(xv)] | Yes |
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)] | 19.2062769 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0324684 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000285 |
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)] | TX DEHY30 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 5.69 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.92 |
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)] | 1.1 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 1.2614748 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0058573 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000025 |
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)] | TX DEHY31 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 8.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 43.28 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.17 |
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)] | 1.3 |
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)] | 8784 |
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)] | 665 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 8.3766268 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 56.9421774 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY32 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 8.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 43.28 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.17 |
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)] | 1.3 |
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)] | 8784 |
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)] | 665 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 8.3914767 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 57.0159461 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY33 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 8.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 43.28 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.17 |
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)] | 1.3 |
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)] | 8784 |
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)] | 665 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 8.3766268 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 56.9421774 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY34 |
County and State [98.236(e)(1)(xviii)] | ZAPATA, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 8.5 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 43.28 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.17 |
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)] | 1.3 |
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)] | 8784 |
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)] | 665 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.01849 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.94534 |
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)] | 8.3766268 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 56.9421774 |
Unit ID or Name [98.236(e)(1)(i)] | TX DEHY35 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 9.336 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.4 |
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)] | 1.1 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 1.2213429 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0056866 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000024 |
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)] | TX DEHY36 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 10.007 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.49 |
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)] | 1.1 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 1.216465 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0056686 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000024 |
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)] | TX DEHY37 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 10.203 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.52 |
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)] | 1.1 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 1.216463 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0056686 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000024 |
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)] | TX DEHY38 |
County and State [98.236(e)(1)(xviii)] | REFUGIO, TX |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 11.144 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.86 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.77 |
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)] | 2.8 |
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)] | 1050 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00425 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.97287 |
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)] | 3.213244 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.0149036 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000064 |
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)] | TX DEHY39 |
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)] | 24 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 32.67 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.63 |
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)] | 1.63 |
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)] | 71 |
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)] | 0.0209 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.91683 |
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)] | 419.2182556 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 2.4106961 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.000883 |
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)] | 5.1751997 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 2.2341605 |
Unit ID or Name [98.236(e)(1)(i)] | LA DEHY1 |
County and State [98.236(e)(1)(xviii)] | ST MARY, LA |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 8.3664688 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 41.73 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.6 |
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)] | 2.77 |
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)] | 8720 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 82 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 760 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.02023 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.091897 |
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)] | 492.1529362 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 2.7236811 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0010173 |
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)] | LA DEHY2 |
County and State [98.236(e)(1)(xviii)] | VERMILION, LA |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.2894411 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 34.66 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 1.79 |
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)] | 0.27 |
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)] | 6528 |
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)] | 900 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.02175 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.93775 |
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)] | 42.4620589 |
CH4 Emissions from Flares or Regenerators (mt CH4) [98.236(e)(1)(xvi)(B)] | 0.2479064 |
N2O Emissions from Flares or Regenerators (mt N2O) [98.236(e)(1)(xvi)(C)] | 0.0000904 |
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)] | LA DEHY3 |
County and State [98.236(e)(1)(xviii)] | CAMERON, LA |
Glycol dehydrator feed natural gas flow rate determined by engineering estimate based on best available data (MMscfd) [98.236(e)(1)(ii)] | 2.974484 |
Dehydrator feed natural gas water content (pounds per MMscf) [98.236(e)(1)(iii)] | 45.94 |
Dehydrator outlet natural gas water content (pounds per MMscf) [98.236(e)(1)(iv)] | 2.9 |
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)] | 0.33 |
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)] | 7583 |
Temperature of the wet natural gas (°F) [98.236(e)(1)(xi)] | 95 |
Pressure of the wet natural gas (psig) [98.236(e)(1)(xii)] | 1152 |
Concentration of CO2 in wet natural gas (mole fraction) [98.236(e)(1)(xiv)] | 0.00744 |
Concentration of CH4 in wet natural gas (mole fraction) [98.236(e)(1)(xiii)] | 0.915 |
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)] | 1.091572 |
CH4 Emissions from Venting (mt CH4) [98.236(e)(1)(xvii)(B)] | 21.6257133 |
County and State [98.236(j)(1)(i)] | CAMERON, LA |
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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 150 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 75 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 43.425 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 10 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.243846 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.529731 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.007355 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.1388501 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 6.6117091 |
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)] | 66313.67 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 10 |
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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 52.390321 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 16 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.4719936 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 14.6958173 |
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)] | 151683.39 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 16 |
County and State [98.236(j)(1)(i)] | WHARTON, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 57.608 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 4 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.0563731 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 1.7552109 |
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)] | 18116.47 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 4 |
County and State [98.236(j)(1)(i)] | FORT BEND, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 52.6028571 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 46 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.1827128 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 5.6888778 |
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)] | 58717.95 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 46 |
County and State [98.236(j)(1)(i)] | DUVAL, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 28.92 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 14 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.202404 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 6.3019765 |
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)] | 65046.07 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 14 |
County and State [98.236(j)(1)(i)] | JEFFERSON, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 42.7222222 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 26 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.089494 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 2.7864519 |
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)] | 28760.46 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 26 |
County and State [98.236(j)(1)(i)] | GALVESTON, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 40.1885 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 12 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.2212876 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 6.8899288 |
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)] | 71114.64 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 12 |
County and State [98.236(j)(1)(i)] | HIDALGO, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 52.487 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 29 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.1508258 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 4.6960554 |
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)] | 48470.5 |
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)] | Yes |
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)] | 32 |
County and State [98.236(j)(1)(i)] | SAN JACINTO, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 50.1272727 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 9 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.0360351 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 1.1219765 |
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)] | 11580.52 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 9 |
County and State [98.236(j)(1)(i)] | BRAZORIA, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 53.3097561 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 18 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.2456352 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 7.6480079 |
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)] | 78939.18 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 18 |
County and State [98.236(j)(1)(i)] | STARR, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 45.1380952 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 11 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.1420418 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 4.4225612 |
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)] | 45647.62 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 11 |
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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 45.6136364 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 2 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.0725778 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 2.2597569 |
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)] | 23324.16 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 2 |
County and State [98.236(j)(1)(i)] | ARANSAS, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 57.8125 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 10 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.0781475 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 2.4331711 |
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)] | 25114.06 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 10 |
County and State [98.236(j)(1)(i)] | REFUGIO, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 39.2161616 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 61 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 3.0322186 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 94.4100363 |
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)] | 974456.48 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 61 |
County and State [98.236(j)(1)(i)] | ORANGE, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 47.175 |
Count of tanks that vented directly to the atmosphere [98.236(j)(1)(xiii)(A)] | 7 |
Minimum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.32959 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0.329594 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0.00386 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0.003864 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0.0550189 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 1.7130485 |
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)] | 17681.29 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 7 |
County and State [98.236(j)(1)(i)] | MATAGORDA, 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 Tanks 2.0 |
Average gas-liquid separator or non-separator equipment temperature (°F) [98.236(j)(1)(iv)] | 77 |
Average gas-liquid separator or non-separator equipment pressure (psig) [98.236(j)(1)(v)] | 32.5 |
Average sales oil or stabilized oil API gravity (degrees) [98.236(j)(1)(vi)] | 0 |
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 |
Maximum concentration of CH4 in flash gas (mole fraction) [98.236(j)(1)(viii)] | 0 |
Minimum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)]] | 0 |
Maximum concentration of CO2 in flash gas (mole fraction) [98.236(j)(1)(vii)] | 0 |
Annual CO2 emissions from venting (mt CO2) [98.236(j)(1)(xiii)(B)] | 0 |
Annual CH4 emissions from venting (mt CH4) [98.236(j)(1)(xiii)(C)] | 0 |
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)] | 0 |
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)] | No |
Count of atmospheric tanks [98.236(j)(1)(x)] | 3 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | LAFLARE1 |
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)] | 168336 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.91897 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.02023 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 9.4679186 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.0594032 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000208 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | LAFLARE2 |
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)] | 177912 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.90898 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.05462 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 9.708105 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.0620999 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.000022 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE1 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE2 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE3 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE4 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE5 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE6 |
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)] | 3091968 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8129187 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.006322 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE7 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE8 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE9 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE10 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE11 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE12 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE13 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE14 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE15 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE16 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE17 |
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)] | 184464 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.92197 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.00131 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE18 |
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)] | 4339296 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8358246 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0352913 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE19 |
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)] | 229701.6 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8278382 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0593465 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE20 |
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)] | 2968992 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8000751 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0422855 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE21 |
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)] | 415483.2 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.6128366 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.1712814 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |
Unique Name or ID Number for the Flare Stack [98.236(n)(1)] | TXFLARE22 |
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)] | 7334640 |
Flare combustion efficiency (decimal value) [98.236(n)(6)] | 0.98 |
Mole fraction of CH4 in flare feed gas, XCH4 [98.236(n)(7)] | 0.8791058 |
Mole fraction of CO2 in flare feed gas, XCO2 [98.236(n)(8)] | 0.0415616 |
Fraction of feed gas sent to un-lit flare, Zu [98.236(n)(5)] | 0 |
CO2 emissions (mt CO2) [98.236(n)(9)] | 10.8131296 |
CH4 Emissions (mt CH4) (Eq. W-19) [98.236(n)(10)] | 0.065307 |
N2O Emissions (mt N2O) (Eq. W-40) [98.236(n)(11)] | 0.0000228 |