CO2 equivalent emissions from facility subparts C-II, SS, and TT (metric tons):619,920.5
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:2016-01-01
GHG Report End Date:2016-12-31
Description of Changes to Calculation Methodology:
Plant Code Indicator:N
Primary NAICS Code:325120
Second Primary NAICS Code:325211
Additional NAICS Codes: 326130
Parent Company Details:
Parent Company Name:THE CHEMOURS CO
Address:1007 N. Market Street,
Wilmington,
DE 19898
Percent Ownership Interest:100
Subpart C: General Stationary Fuel Combustion
Gas Information Details
| Gas Name | Carbon Dioxide |
| Gas Quantity | 38,326.5 (Metric Tons) |
| Own Result? | |
| Gas Name | Biogenic Carbon dioxide |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | Methane |
| Gas Quantity | 0.72 (Metric Tons) |
| Own Result? | |
| Gas Name | Nitrous Oxide |
| Gas Quantity | 0.072 (Metric Tons) |
| Own Result? | |
Unit Details:
Unit Name : GP-Boilers
Unit Type : OCS (Other combustion source)
Unit Description :
Other Unit Name :
Small Unit Aggregation Details:
Use Ivt Indicator: N
Highest Maximum Rated Heat Input Capacity:
139.4
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:
38366.0
(metric tons)
Tier Fuel Details:
Fuel :
Natural Gas (Weighted U.S. Average)
Tier Name :
Tier 1 (Equation C-1)
Tier Methodology Start Date :
2016-01-01
Tier Methodology End Date :
2016-12-31
Fuel Emission Details :
| Total CO2 emissions | Total CH4 emissions | Total N2O emissions | Total CH4 emissions CO2e | Total N2O emissions CO2e |
|
38324.4
(Metric Tons)
|
0.72
(Metric Tons)
|
0.072
(Metric Tons)
|
18.1
(Metric Tons)
|
21.5
(Metric Tons)
|
Equation C1/C8 Inputs :
Fuel Quantity :
703980000
(scf/year)
Fuel :
Distillate Fuel Oil No. 2
Tier Name :
Tier 1 (Equation C-1)
Tier Methodology Start Date :
2016-01-01
Tier Methodology End Date :
2016-12-31
Fuel Emission Details :
| Total CO2 emissions | Total CH4 emissions | Total N2O emissions | Total CH4 emissions CO2e | Total N2O emissions CO2e |
|
2.1
(Metric Tons)
|
0.00
(Metric Tons)
|
0.000
(Metric Tons)
|
0
(Metric Tons)
|
0
(Metric Tons)
|
Equation C1/C8 Inputs :
Fuel Quantity :
201
(gallons/year)
Subpart L: Fluorinated Gas Production
Gas Information Details
| Gas Name | Other |
| Other Gas Name | CO2 equivalent (from unspecified gases) |
| Gas Quantity | 581,554.5 (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 |
| 2H-perfluoro(5-methyl-3,6-dioxanonane) | C8HF17O2 | 3330-14-1 | | 5.5073 | |
| Perfluoro(methylcyclopropane) | C4F8 | 379-16-8 | | 14.8316 | |
| Carbonic difluoride | CF2O | 353-50-4 | | 1.5588 | |
| [[difluoro(trifluoromethoxy)methoxy]difluoromethoxy]difluoro-acetyl fluoride | C5 F10 O4 | 21703-45-7 | Other fluorinated GHGs | 0.5812 | |
| Trifluoroacetyl fluoride | C2F4O | 354-34-7 | | 1.2483 | |
| Hexafluoropropylene oxide | C3F6O | 428-59-1 | | 23.5009 | |
| HFC-23 | CHF3 | 75-46-7 | | 6.6688 | |
| Perfluoro-2-(2-Fluorosulfonylethoxy) Propyl Vinyl Ether | C7F14O4S | 16090-14-5 | | 2.7651 | |
| 2,3,3,3-tetrafluoro-2-(trifluoromethoxy) propionyl fluoride | | 2927-83-5 | Other fluorinated GHGs | 0.6134 | |
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 |
| Hexafluoropropylene oxide | C3F6O | 428-59-1 | | 7.3002 | |
| Perfluoropropyl vinyl ether | C5F10O | 1623-05-8 | | 0.2336 | |
| Propanoic Acid, 3-[1-[Difluoro [ (Trifluoroethenyl oxy] Methyl]-1,2,2,2-Tetrafluoroethoxy] -2,2,3,3-Tetrafluoro-, Methyl Ester | C9 H3 F13 O4 | 63863-43-4 | | 0.0001 | |
| 2,3,3,3-Tetrafluoro-2-(heptafluoropropoxy)propanoyl fluoride | C6F12O2 | 2062-98-8 | | 0.0001 | |
| PMVE; HFE-216 | CF3OCF=CF2 | 1187-93-5 | | 23.2032 | |
| Perfluoroethyl vinyl ether | C4F8O | 10493-43-3 | | 0.2577 | |
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 |
| ISO_Container__/__17,000_L | | No | | | | |
| UNT_Cylinder__/__1,000_L | | No | | | | |
| 1-Ton_Cylinder__/__760_L | | No | | | | |
| 3AA_Cylinder__/__50_L | | No | | | | |
| 4BW_Cylinder__/__450_L | | No | | | | |
| ISO_container__/__1700_L | | 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 | 1808.2269 | |
| Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones | 4.9954 | |
| Saturated HFCs with 3 or more carbon-hydrogen bonds | 136.1261 | |
| Fluorinated acetates, carbonofluoridates, and fluorinated alcohols other than fluorotelomer alcohols | 21.5125 | |
| Saturated HFEs and HCFEs with 3 or more carbon-hydrogen bonds | 5.5592 | |
Production and Transformation Processes
| Unique Name/Identifier | HFPO Process |
| 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. | >=0% to <75% |
Process Vent Emissions
| 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 | Yes |
| 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) | 282659.2 |
| Effective destruction efficiency range (CO2e basis) | |
| 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 | Yes |
| 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) | 0.8 |
| 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 | Yes |
| 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) | 97542.0 |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 4299.7 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Fluorinated acetates, carbonofluoridates, and fluorinated alcohols other than fluorotelomer alcohols |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 17.4 |
| 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 | Fully fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 3337.9 |
| 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 | Yes |
| 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 | |
| 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 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 | Yes |
| 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 | |
| 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) | 1156.2 |
| 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 | Yes |
| 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 | |
| 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) | 165.2 |
| Fluorinated GHG Group | Fluorinated acetates, carbonofluoridates, and fluorinated alcohols other than fluorotelomer alcohols |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 0.3 |
| 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 | VE North Process |
| Process Type | Transformation 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 | 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 1.9 |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 79536.3 |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 70.3 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated HFEs and HCFEs with 3 or more carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | Yes |
| Process Vent Specific Emission Factor | |
| 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 | Fluorinated acetates, carbonofluoridates, and fluorinated alcohols other than fluorotelomer alcohols |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | Yes |
| Process Vent Specific Emission Factor | |
| 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) | |
| 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 | Yes |
| 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 | |
| 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) | 0.3 |
| 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 | Yes |
| 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 | |
| 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) | 1946.5 |
| 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 | Yes |
| 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 | |
| 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) | 1237.8 |
| Fluorinated GHG Group | Saturated HFEs and HCFEs with 3 or more carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 4.7 |
| Fluorinated GHG Group | Fluorinated acetates, carbonofluoridates, and fluorinated alcohols other than fluorotelomer alcohols |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 3.8 |
| 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 | VE South Process |
| Process Type | Transformation 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. | >=99% |
Process Vent Emissions
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 3057.3 |
| Effective destruction efficiency range (CO2e basis) | |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 0.9 |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 12032.2 |
| 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 | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 968.7 |
| 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 | Yes |
| 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 | |
| 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) | 0.3 |
| 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 | Yes |
| 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 | |
| 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) | 3812.4 |
| 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 | RSU Process |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | Yes |
| Packaging | |
| Optional Comments | |
| The range (Table L-2) that encompasses the effective destruction efficiency, DEeffective, calculated for this process using Equation L-35. | >=99% |
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 | Yes |
| Process Vent Specific Emission Factor | |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 32.9 |
| 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 | Yes |
| 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 | |
| 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 | Yes |
| 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 | |
| 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) | 2.9 |
| 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 | MMF Process |
| Process Type | Transformation |
| Characterize the process: |
| Reaction | Yes |
| Distillation | Yes |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| 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 | Saturated HFEs and HCFEs with 3 or more carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 0.8 |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 5.5 |
| Effective destruction efficiency range (CO2e basis) | |
| Fluorinated GHG Group | Saturated HFCs with 3 or more carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 129.0 |
| 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 | Yes |
| 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 | |
| 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 HFEs and HCFEs with 3 or more carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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 | Yes |
| 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 | |
| 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) | 20.2 |
| Fluorinated GHG Group | Saturated HFCs with 3 or more carbon-hydrogen bonds |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 7.2 |
| 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 | Resins Process |
| 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. | >=0% to <75% |
Process Vent Emissions
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 14825.7 |
| Effective destruction efficiency range (CO2e basis) | |
| 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 | Yes |
| Process Vent Specific Emission Factor | |
| 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) | |
| 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 | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 1647.3 |
| 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 | Yes |
| 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 | |
| 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 |
| 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 | PPA Process |
| Process Type | Transformation 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 | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from process vents | |
| Process Vent Emission Calculation Factor | Yes |
| Process Vent Specific Emission Factor | |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 20.7 |
| 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 | Other fluorinated GHGs |
| Methods used to determine the mass emissions of each fluorinated GHG group emitted from equipment leaks | |
| Average EF Approach | Yes |
| 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 | |
| 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) | 2.3 |
| 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 | |