CO2 equivalent emissions from facility subparts C-II, SS, and TT (metric tons):771,753.1
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:2022-01-01
GHG Report End Date:2022-12-31
Description of Changes to Calculation Methodology:
Plant Code Indicator:N
Primary NAICS Code:325211
Second Primary NAICS Code:325120
Parent Company Details:
Parent Company Name:DAIKIN HOLDINGS AMERICA INC
Address:9920 Corporate Campus Drive, Suite 2200,
Louisville,
KY 40223
Percent Ownership Interest:100
Subpart C: General Stationary Fuel Combustion
Gas Information Details
| Gas Name | Carbon Dioxide |
| Gas Quantity | 45,504 (Metric Tons) |
| Own Result? | |
| Gas Name | Biogenic Carbon dioxide |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | Methane |
| Gas Quantity | 0.86 (Metric Tons) |
| Own Result? | |
| Gas Name | Nitrous Oxide |
| Gas Quantity | 0.086 (Metric Tons) |
| Own Result? | |
Unit Details:
Unit Name : GP-DAIKIN FG Units
Unit Type : OCS (Other combustion source)
Unit Description :
Other Unit Name :
Small Unit Aggregation Details:
Use Ivt Indicator: Y
Highest Maximum Rated Heat Input Capacity:
73.8
Cumulative Maximum Rated Heat Input Capacity:
167.9
Emission Details:
Annual CO2 mass emissions from sorbent: 0 (Metric Tons)
Annual Biogenic CO2 Emissions:
0
(metric tons)
Annual Fossil fuel based CO2 Emissions:
45504
(metric tons)
Tier Fuel Details:
Fuel :
Natural Gas (Weighted U.S. Average)
Tier Name :
Tier 2 (Equation C-2a)
Tier Methodology Start Date :
2022-01-01
Tier Methodology End Date :
2022-12-31
Frequency of HHV determinations :
Other (specify)
Other specified frequency of HHV determinations :
Annually
Tier 2 Monthly HHV Details :
| January | February | March | April | May | June | July | August | September | October | November | December |
|
N
|
N
|
N
|
N
|
N
|
N
|
N
|
N
|
N
|
N
|
N
|
N
|
Fuel Emission Details :
| Total CO2 emissions | Total CH4 emissions | Total N2O emissions | Total CH4 emissions CO2e | Total N2O emissions CO2e |
|
45504.0
(Metric Tons)
|
0.86
(Metric Tons)
|
0.086
(Metric Tons)
|
21.4
(Metric Tons)
|
25.6
(Metric Tons)
|
Subpart L: Fluorinated Gas Production
Gas Information Details
| Gas Name | Other |
| Other Gas Name | CO2 equivalent (from unspecified gases) |
| Gas Quantity | 722,302.6 (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 |
| Perfluorocyclobutane | C-C4F8 | 115-25-3 | | 66.8853 | |
| HFE-449sl, (HFE-7100) Isomer blend | C4F9OCH3, (CF3)2CFCF2OCH3 | 163702-07-6, 163702-08-7 | | 7.7301 | |
| PFC-116 (Perfluoroethane) | C2F6 | 76-16-4 | | 2.0776 | |
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 |
| HFC-134a | CH2FCF3 | 811-97-2 | | 0.89 | |
| HFC-32 | CH2F2 | 75-10-5 | | 0.89 | |
| HFC-125 | C2HF5 | 354-33-6 | | 0.89 | |
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 | | No | | | | |
Production and Transformation Process GHG Group Emissions
| Fluorinated GHG Group | Production and transformation process GHG group emissions (metric tons CO2e) | Optional Comments |
| Unsaturated perfluorocarbons (PFCs), unsaturated HFCs, unsaturated hydrochlorofluorocarbons (HCFCs), unsaturated halogenated ethers, unsaturated halogenated esters, fluorinated aldehydes, and fluorinated ketones | 19.2514 | |
| Saturated HFEs and HCFEs with 3 or more carbon-hydrogen bonds | 255.3235 | |
| Saturated hydrofluorocarbons (HFCs) with 2 or fewer carbon-hydrogen bonds | 478.4442 | |
Production and Transformation Processes
| Unique Name/Identifier | TFE Manufacturing |
| Process Type | Production Process |
| 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 | 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) | 18.9 |
| 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 | |
| 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 | 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 | |
| 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 | |
| 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) | 2.3 |
| 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 | 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 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 34455.1 |
| 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 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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 | 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 | |
| Screening Ranges Approach w/ M21 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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 | |
| Screening Ranges Approach w/ M21 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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 |
| 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 | HFP Manufacturing |
| Process Type | Transformation Process |
| 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 | 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) | 11.6 |
| 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) | 0.0 |
| 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 | |
| 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) | 2.3 |
| 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) | 7.2 |
| 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 | 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 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 10893.5 |
| 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 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 1.0 |
| 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 | |
| Screening Ranges Approach w/ M21 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 79.2 |
| 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 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 468.9 |
| 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 | PTFE Manufacturing |
| Process Type | Transformation Process |
| 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 | 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) | 0.1 |
| 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 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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 |
| 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 | Melt Resin Production |
| 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 | 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) | 406744.9 |
| 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) | 6.7 |
| 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 | Yes |
| GWP-weighted mass of all fluorinated GHGs in this group emitted from all process vents combined (metric tons CO2e) | 1084.4 |
| 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 | |
| Screening Ranges Approach w/ M21 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 262140.7 |
| 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 | |
| Screening Ranges Approach w/ M21 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 11.2 |
| 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 | |
| Screening Ranges Approach w/ M21 | Yes |
| EPA Correlation Approach w/ M21 | Yes |
| 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) | 1384.4 |
| 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 | |
Subpart O: HCFC-22 Production and HFC-23 Destruction
Gas Information Details
| Gas Name | Carbon Dioxide |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | Biogenic Carbon dioxide |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | Methane |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | Nitrous Oxide |
| Gas Quantity | 0 (Metric Tons) |
| Own Result? | |
| Gas Name | HFC-23 |
| Gas CAS Registry Number | 75-46-7 |
| Gas Linear Chemical Formula | CHF3 |
| Gas Quantity | 0.263468 (Metric Tons) |
| Own Result? | |
Subpart O Facility Information:
| Indicate whether your facility produces HCFC-22 | Y
|
| 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:
| Production Process Name or ID | R22 Production Process
|
| For HCFC-22 producers, how do you estimate your HFC-23 emissions(Both indicates Equation O-4 and Equation O-5 are used) | Equation O-5
|
| Annual mass of HCFC-22 produced | ()
|
| Reactants Fed into the Process |
| Reactant Name | Annual mass of reactant fed into the process | Indicate whether the annual mass of the reactant fed into the process is based on a missing data procedure | Parameter for which missing data were used | Other parameter | Number of hours that a missing data procedure was used to determine the annual mass of the reactant fed into the process |
| ()
| N | | | |
| ()
| N | | | |
|
| The combined mass of all materials other than HCFC-22 and HFC-23 (i.e., unreacted reactants, HCI and other by-products) that occur in more than trace concentrations and
that are permanently removed from the process
| ()
|
| Indicate whether the annual mass of combined mass of all materials other than HCFC-22 and HFC-23 at the facility is based on a missing data procedure | N
|
| Number of hours that a missing data procedure was used to determine the annual mass of combined mass of all materials other than HCFC-22 and HFC-23 |
|
| Method for tracking startups, shutdowns, and malfunctions and HFC-23 generation/emissions during these events | T-Thermal CISWI unit has full DCS and PLC controls and interlocks in place to prevent emissions.
|
| Annual HFC-23 Emissions from the Facility Calculated Using Equation O-4 | ()
|
| Annual mass of HFC-23 emitted from all equipment leaks at the facility | 0.003627 (Metric Tons)
|
| Was the annual mass of HFC-23 emitted from all equipment leaks at the facility based on a missing data procedure? | N
|
| Annual mass of HFC-23 emitted from all process vents at the facility | 0.259841 (Metric Tons)
|
| Was the annual mass of HFC-23 emitted from all process vents at the facility based on a missing data procedure? | N
|
| Annual HFC-23 Emissions from the Facility Calculated Using Equation O-5 | 0.263468 (Metric Tons)
|
Destruction Processes Connected to the HCFC-22 Production Equipment
| Unique Name/Identifier of destruction process connected to the HCFC-22 production equipment | Daikin T-Thermal Incinerator
|
| Description of Destruction Process | CISWI Daikin T-Thermal Incinerator
|
| Was the HFC-23 fed into the on-site destruction process originally generated by an on-site HCFC-22 production process? | Y
|
| 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
(mass fraction)
|
| Is the concentration below the detection limit? | N
|
| Detection limit concentration |
()
|
| Detection limit concentration units |
|
| 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) | 0.545636 (Metric Tons)
|
Off-Site Destruction Facility:
On-Site Destruction Process (only destruction devices that are not directly connected to HFC-22 production equipment)
| Unique Name/Identifier | T-Thermal Incinerator
|
| 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
(mass fraction)
|
| Is the concentration below the detection limit? | N
|
| Detection limit concentration |
()
|
| Detection limit concentration units |
|
| 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) | 0.545636 (Metric Tons)
|