CO2 equivalent emissions from facility subparts C-II, SS, and TT (metric tons):782,392.1
CO2 equivalent emissions from supplier subparts LL-QQ (metric tons):
Biogenic CO2 emissions from facility subparts C-II, SS, and TT (metric tons):0
Cogeneration Unit Emissions Indicator:N
GHG Report Start Date:2023-01-01
GHG Report End Date:2023-12-31
Description of Changes to Calculation Methodology:Continuing calculations using methodologies employed for the last year calculations. New compounds will be reported as they are determined to be present and when estimation methods for their discharge maybe developed.
Plant Code Indicator:N
Primary NAICS Code:325211
Second Primary NAICS Code:325120
Parent Company Details:
Parent Company Name:THE CHEMOURS CO
Address:1007 Market Street,
Wilmington,
DE 19898
Percent Ownership Interest:100
Subpart C: General Stationary Fuel Combustion
Gas Information Details
| Gas Name | Carbon Dioxide |
| Gas Quantity | 186,491 (Metric Tons) |
| Own Result? | |
| Gas Name | Biogenic Carbon dioxide |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | Methane |
| Gas Quantity | 3.51 (Metric Tons) |
| Own Result? | |
| Gas Name | Nitrous Oxide |
| Gas Quantity | 0.351 (Metric Tons) |
| Own Result? | |
Unit Details:
Unit Name : GP-A
Unit Description :
Small Unit Aggregation Details:
Use Ivt Indicator: Y
Highest Maximum Rated Heat Input Capacity:
0
Cumulative Maximum Rated Heat Input Capacity:
Emission Details:
Annual CO2 mass emissions from sorbent: 0 (Metric Tons)
Annual Biogenic CO2 Emissions:
0
(metric tons)
Annual Fossil fuel based CO2 Emissions:
0
(metric tons)
Tier Fuel Details:
Fuel :
Bituminous
Tier Name :
Tier 1 (Equation C-1)
Tier Methodology Start Date :
2023-01-01
Tier Methodology End Date :
2023-12-31
Fuel Emission Details :
| Total CO2 emissions | Total CH4 emissions | Total N2O emissions | Total CH4 emissions CO2e | Total N2O emissions CO2e |
|
0
(Metric Tons)
|
0
(Metric Tons)
|
0
(Metric Tons)
|
0
(Metric Tons)
|
0
(Metric Tons)
|
Unit Name : GP-B
Unit Description :
Small Unit Aggregation Details:
Use Ivt Indicator: Y
Highest Maximum Rated Heat Input Capacity:
249
Cumulative Maximum Rated Heat Input Capacity:
928
Emission Details:
Annual CO2 mass emissions from sorbent: 0 (Metric Tons)
Annual Biogenic CO2 Emissions:
0
(metric tons)
Annual Fossil fuel based CO2 Emissions:
186491.0
(metric tons)
Tier Fuel Details:
Fuel :
Natural Gas (Weighted U.S. Average)
Tier Name :
Tier 1 (Equation C-1b, natural gas billing in mmBtu)
Tier Methodology Start Date :
2023-01-01
Tier Methodology End Date :
2023-12-31
Fuel Emission Details :
| Total CO2 emissions | Total CH4 emissions | Total N2O emissions | Total CH4 emissions CO2e | Total N2O emissions CO2e |
|
186491.0
(Metric Tons)
|
3.51
(Metric Tons)
|
0.351
(Metric Tons)
|
87.9
(Metric Tons)
|
104.7
(Metric Tons)
|
Subpart L: Fluorinated Gas Production
Gas Information Details
| Gas Name | Other |
| Other Gas Name | CO2 equivalent (from unspecified gases) |
| Gas Quantity | 595,708.7 (Metric Tons) |
| Own Result? | |
Summary Information
| Did the facility produce only one fluorinated gas product, including fluorinated gas products that are intermediates? | No |
| Did the facility emit 1,000 or more metric tons of CO2e of any one fluorinated GHG from production and transformation processes, summed across the facility as a whole? | Yes |
| Did the facility destroy previously produced fluorinated GHGs in destruction processes that are not part of a fluorinated gas production process or fluorinated gas transformation process? | No |
| Did the facility vent residual fluorinated GHGs from containers? | Yes |
Production and Transformation Process F-GHG Emissions
| Gas Name | Gas Description | CAS No. | GWP Group | Production and transformation process F-GHG emissions (metric tons) | Optional Comments |
| Perfluorohexadecane | C16F34 | 355-49-7 | Fully fluorinated GHGs | 0.2414 | |
| HEPTAFLUOROPROPYL TRIFLUOROMETHYL ETHER | C4F10O | 59426-77-6 | | 0.6996 | |
| Chlorodifluoromethane | CHF2Cl | 75-45-6 | Other fluorinated GHGs | 10.8206 | |
| Perfluorocyclobutane | C-C4F8 | 115-25-3 | | 28.3324 | |
| 1H,8H-Perfluorooctane | HCF2(CF2)6CF2H | 307-99-3 | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds | 0.5268 | |
| PFC-116 (Perfluoroethane) | C2F6 | 76-16-4 | | 2.1079 | |
| Chloropentafluoroethane | CClF2CF3 | 76-15-3 | Other fluorinated GHGs | 0.7366 | |
| 1,1,1,2,2,3,3-Heptafluoro-3-(1,2,2,2-tetrafluoroethoxy)-propane | CF3CF2CF2OCHFCF3 | 3330-15-2 | | 6.5914 | |
| Nitrogen trifluoride | NF3 | 7783-54-2 | | 0.0588 | |
| 1H,6H-Perfluorohexane | HCF2CF2CF2CF2CF2CF2H | 366-07-2 | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds | 0.9219 | |
| HFC-23 | CHF3 | 75-46-7 | | 12.0885 | |
| PFC-218 (Perfluoropropane) | C3F8 | 76-19-7 | | 0.5477 | |
| 1H,4H-Perfluorobutane | HCF2CF2CF2CF2H | 377-36-6 | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds | 1.1853 | |
| HFE-125 | CHF2OCF3 | 3822-68-2 | | 0.3628 | |
Venting of Residual F-GHGs
| Gas Name | Gas Description | CAS No. | GWP Group | Fluorinated F-GHGs vented from containers returned from the field (metric tons): | Optional Comments |
| PFC-1216; Dyneon HFP | C3F6; CF3CF=CF2 | 116-15-4 | | 13.9535 | |
Container Information
| Container name | Description (optional) | Was based on a missing data procedure? | Data element for which missing data procedures were used, and the reason for the missing data | Number of hours a missing data procedure was used to determine F-GHG emissions from container | Provide the method used to estimate the missing data | If the data element is reportable under subpart L, provide estimates of the missing data |
| Ton_Cylinder | | No | | | | |
| ISO_Container_or_Tank_Truck | | No | | | | |
| 75_Pounds_Cylinder | | No | | | | |
| Tank_Car | | No | | | | |
Production and Transformation Process GHG Group Emissions
| Fluorinated GHG Group | Production and transformation process GHG group emissions (metric tons CO2e) | Optional Comments |
| Other fluorinated GHGs | 1228.7766 | |
| Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds | 1680.8713 | |
| Fluorinated GHGs with carbon-iodine bond(s) | 0.6225 | |
| Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones | 16.6586 | |
| Fully fluorinated GHGs | 29.5607 | |
Production and Transformation Processes
| Unique Name/Identifier | P2 |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | |
| Packaging | |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=75% to <95% |
Process Vent Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 2.8 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 15739.8 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 12.9 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 6711.2 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 13033.9 |
| Effective destruction efficiency range (CO2e basis) | |
| Were the annual emissions of one or more F-GHG groups based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from process vents | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of missing data | |
Equipment Leak Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.1 |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 314.8 |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.1 |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 131.0 |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 23.1 |
| Were the annual emissions from equipment leaks based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from equipment leaks | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of the missing data | |
| Unique Name/Identifier | P5 |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | |
| Packaging | |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=0% to <75% |
Process Vent Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 0.0 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 30.7 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 7590.6 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 38.4 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 2.8 |
| Effective destruction efficiency range (CO2e basis) | |
| Were the annual emissions of one or more F-GHG groups based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from process vents | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of missing data | |
Equipment Leak Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.0 |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.6 |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 144.1 |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.8 |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.0 |
| Were the annual emissions from equipment leaks based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from equipment leaks | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of the missing data | |
| Unique Name/Identifier | P6 |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | |
| Packaging | |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=0% to <75% |
Process Vent Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 0.2 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 1929.0 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 23718.1 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 2678.1 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 1969.1 |
| Effective destruction efficiency range (CO2e basis) | |
| Were the annual emissions of one or more F-GHG groups based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from process vents | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of missing data | |
Equipment Leak Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.0 |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 38.6 |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 474.8 |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 53.5 |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 59.1 |
| Were the annual emissions from equipment leaks based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from equipment leaks | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of the missing data | |
| Unique Name/Identifier | P4 |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | Yes |
| Packaging | Yes |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=75% to <95% |
Process Vent Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 0.7 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 21177.5 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 5247.6 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 280397.7 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 174482.7 |
| Effective destruction efficiency range (CO2e basis) | |
| Were the annual emissions of one or more F-GHG groups based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from process vents | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of missing data | |
Equipment Leak Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.0 |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 630.0 |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 157.4 |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 8411.1 |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 22.6 |
| Were the annual emissions from equipment leaks based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from equipment leaks | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of the missing data | |
| Unique Name/Identifier | P3 |
| Process Type | Production Process |
| Characterize the process: |
| Reaction | Yes |
| Distillation | Yes |
| Packaging | Yes |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=0% to <75% |
Process Vent Emissions
| Fluorinated GHG Group | Fluorinated GHGs with carbon-iodine bond(s) |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 0.6 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 19.3 |
| Effective destruction efficiency range (CO2e basis) | |
| Were the annual emissions of one or more F-GHG groups based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from process vents | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of missing data | |
Equipment Leak Emissions
| Fluorinated GHG Group | Fluorinated GHGs with carbon-iodine bond(s) |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.0 |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.2 |
| Were the annual emissions from equipment leaks based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from equipment leaks | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of the missing data | |
| Unique Name/Identifier | P1 |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | |
| Packaging | |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=0% to <75% |
Process Vent Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 12.3 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 296.1 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 5163.0 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 3.3 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | |
| Process Vent Specific Emission Factor | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 24448.0 |
| Effective destruction efficiency range (CO2e basis) | |
| Were the annual emissions of one or more F-GHG groups based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from process vents | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of missing data | |
Equipment Leak Emissions
| Fluorinated GHG Group | Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.2 |
| Fluorinated GHG Group | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.7 |
| Fluorinated GHG Group | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 65.4 |
| Fluorinated GHG Group | Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 0.0 |
| Fluorinated GHG Group | Saturated hydrofluoroethers (HFEs) and hydrochlorofluoroethers (HCFEs) with 1 carbon-hydrogen bond |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | |
| Screening Ranges Approach w/ M21 | |
| EPA Correlation Approach w/ M21 | |
| Unit Specific Correlation Approach w/ M21 | |
| Screening Ranges Approach w/ Site Specific Leak Monitoring Method | |
| EPA Correlation Approach w/ Site Specific Leak Monitoring Method | Yes |
| Unit Specific Correlation Approach w/ Site Specific Leak Monitoring Method | |
| Other Site Specific Leak Monitoring | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from equipment leaks (metric tons CO2e) | 244.5 |
| Were the annual emissions from equipment leaks based on a missing data procedure? | No |
| Data element for which missing data procedures were used, and the reason for the missing data | |
| Number of hours a missing data procedure was used to determine F-GHG emissions from equipment leaks | |
| Provide the method used to estimate the missing data | |
| If the data element is reportable under subpart L, provide estimates of the missing data | |
Subpart O: HCFC-22 Production and HFC-23 Destruction
Gas Information Details
| Gas Name | HFC-23 |
| Gas CAS Registry Number | 75-46-7 |
| Gas Linear Chemical Formula | CHF3 |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
Subpart O Facility Information:
| Indicate whether your facility produces HCFC-22 | N
|
| Indicate whether your facility sends any HFC-23 offsite for destruction | N
|
| Indicate whether your facility destroys HFC-23 onsite | Y
|
HCFC-22 Production Process Information:
Off-Site Destruction Facility:
On-Site Destruction Process (only destruction devices that are not directly connected to HFC-22 production equipment)
| Unique Name/Identifier | T7IMC - CISWI Unit
|
| Description of Destruction Process |
|
| Was the HFC-23 fed into the on-site destruction process originally generated by an on-site HCFC-22 production process? |
|
| Is the annual mass of HFC-23 fed into the destruction device at the facility based on a missing data procedure? | N
|
| Is the annual mass of HFC-23 emitted from the destruction device at the facility based on a missing data procedure? | N
|
| Concentration of HFC-23 measured at the outlet of the destruction device during the facility's annual HFC-23 concentration measurements at the outlet of the device | 0.005
(mass fraction)
|
| Is the concentration below the detection limit? | Y
|
| Detection limit concentration | 0.01
(mass fraction)
|
| Detection limit concentration units | ppm(V)
|
| Was the HFC-23 concentration measured pursuant to §98.154(l) greater than that measured during the performance test that was the basis for the destruction efficiency?
| N
|
| Indicate the method used to calculate the revised destruction efficiency, specifying whether §98.154(l)(1) or (2) was used |
|
| Have you made changes that affect the HFC-23 destruction efficiency or the methods used to record the quantity destroyed? | N
|
| Methods used to determine destruction efficiency |
|
| Methods used to record the mass of HFC-23 destroyed |
|
| Name of other relevant federal or state regulations that may apply to the destruction process |
|
| Annual mass of HFC-23 emitted from the destruction process (device) | 0.000169 (Metric Tons)
|