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1 | We assess data from two of Tradewater's Verra-certified refrigerant destruction projects in Ghana from 2018 and 2019. Since these data do not include project costs, we cannot use them to sense-check overall cost-effectiveness. Instead, we examined the plausibility of Tradewater’s estimates of (a) counterfactual baseline emissions from destroyed GHG and (b) project emissions. This model was lightly updated in November 2022. The prior version of this model was published in 2021. | Description | 09/11/2018 destruction event | 04/10/2019 destruction event | Units | Source notes | |||||||||||||||||||
2 | Baseline Emissions | ||||||||||||||||||||||||
3 | Quantity of refrigerant destroyed by the project activity: | Key: | Default value from VERRA documents | ||||||||||||||||||||||
4 | - From stockpile | 1.91 | 13.22 | tons of ODS (tODS) of CFC-12 | VCS Monitoring Report for 09-11-2018 event VCS Monitoring Report for 04-10-2019 event | Calculated | |||||||||||||||||||
5 | - From end of life equipment | 0.00 | 0.00 | tODS | Parameters with most uncertainty | ||||||||||||||||||||
6 | Rate of refrigerants (destroyed) which would be vented into the atmosphere in the baseline: | Percentage | Section 9.1 p. 20 of the VCS Methodology (VM0016) | ||||||||||||||||||||||
7 | - From stockpile | 0.00% | 0.00% | ||||||||||||||||||||||
8 | - From end of life equipment | 100.00% | 100.00% | ||||||||||||||||||||||
9 | Emission factor for the rate of refrigerants (destroyed) which would be vented into the atmosphere | 1 | 1 | Value between 0 and 1 | Section 8.1 p.12 of the VCS Methodology (VM0016) | Price per carbon offset (as of Nov 2022) | $17 | ||||||||||||||||||
10 | Rate of refrigerants (destroyed) by the project activity which would also be destroyed in the baseline [%,0-100%] | 0.00% | 0.00% | Percentage | Section 9.1 p. 21 of the VCS Methodology (VM0016) | Total revenue generated | $2,642,980 | ||||||||||||||||||
11 | Emission factor for the rate of refrigerants (destroyed) by the project activity which would also be destroyed in the baseline | 0 | 0 | Value between 0 and 1 | Section 8.1 p.12 of the VCS Methodology (VM0016) | ||||||||||||||||||||
12 | Rate of refrigerants which would remain in, or be recovered and become part of, a stockpile in the baseline | Percentage | Section 9.1 p. 21 of the VCS Methodology (VM0016) | ||||||||||||||||||||||
13 | - From stockpile | 100% | 100% | ||||||||||||||||||||||
14 | - From end of life equipment | 0% | 0% | ||||||||||||||||||||||
15 | Global warming potential of refrigerant type i | 10900 | 10,900 | tCO2e/tODSi | GWP values based on the IPCC Fourth assessment report 2007 - Working group I report “The physical science basis of climate change” - Chapter 2 “Changes in Atmospheric Constituents and in Radiative Forcing” table 2.14/page 212 | ||||||||||||||||||||
16 | Annual emission rate of refrigerant (destroyed), which would remain in, or be recovered and become part of, a stockpile in the baseline | Percentage | Annual emission rates were sourced from the latest version of the Climate Action Reserve’s Article 5 ODS Project Protocol. | ||||||||||||||||||||||
17 | From stockpile | 25% | 25% | ||||||||||||||||||||||
18 | From end of life equipment | 100% | 100% | ||||||||||||||||||||||
19 | Project crediting period | 10 | 10 | Years | |||||||||||||||||||||
20 | Emission factor for the rate of refrigerant (destroyed) which would be reused in the baseline (for stockpile) | 0.944 | 0.944 | Value between 0 and 1 | Section 8.1 p.12 of the VCS Methodology (VM0016) | ||||||||||||||||||||
21 | Emission factor for the rate of refrigerant i (destroyed) which would be reused in the baseline (for end of life equipment) | 1 | 1 | Value between 0 and 1 | Section 8.1 p.12 of the VCS Methodology (VM0016) | ||||||||||||||||||||
22 | Baseline emissions from refrigerants which would be released into the atmosphere in the absence of the project activity in year y | 19,647 | 135,936 | tCO2e | Equation (2) on page 11 of the VCS Methodology (VM0016) | ||||||||||||||||||||
23 | Baseline emissions from blowing agents contained in insulation foams of refrigeration appliances which would be released into the atmosphere in the absence of the project activity. | 0.00 | 0.00 | tCO2e | Section 8.1 p.11 of the VCS Methodology (VM0016) | ||||||||||||||||||||
24 | Total emissions averted | Total quantity of baseline emissions from refrigerants and blowing agents (foam) which would be released into the atmosphere in the absence of the project activity | 19,647 | 135,936 | tCO2e | ||||||||||||||||||||
25 | |||||||||||||||||||||||||
26 | Project Emissions | ||||||||||||||||||||||||
27 | Amount of electricity (MWh) consumed at the ODS recovery facility from the grid | NA | NA | MWh | |||||||||||||||||||||
28 | tons CO2/MWh | NA | NA | tons CO2/MWh | |||||||||||||||||||||
29 | Average technical transmission and distribution losses in the grid for the voltage level at which electricity is obtained from the grid at the project site | NA | NA | % | |||||||||||||||||||||
30 | Project emissions from fossil fuel consumption attributable to the ODS recovery facility including third party used fossil fuel to generate energy for the ODS recovery facility. | NA | NA | tCO2e | |||||||||||||||||||||
31 | Project emissions from electricity consumption from the grid at the ODS recovery facility | NA | NA | tCO2e | |||||||||||||||||||||
32 | Emissions from energy consumption at ODS recovery facility | Project emissions from energy consumption at the ODS recovery facility | tCO2e | ||||||||||||||||||||||
33 | |||||||||||||||||||||||||
34 | Quantity of ODS refrigerant sent for destruction by the project activity, including eligible and ineligible material | 1.91 | 13.22 | tODS for CFC12 | |||||||||||||||||||||
35 | Quantity of ODS blowing agent sent for destruction by the project activity, including eligible and ineligible material | 0 | 0 | tODS | |||||||||||||||||||||
36 | Default emission factor aggregating both transportation and destruction emissions | 7.5 | 7.5 | tCO2 | CAR Article 5 Ozone Depleting Substances Project Protocol Table 6.2 | ||||||||||||||||||||
37 | Emissions from transportation and destruction | Project emission from ODS transportation and destruction | 14.33 | 99.12 | tCO2e | ||||||||||||||||||||
38 | |||||||||||||||||||||||||
39 | Total project emissions | 14.33 | 99.12 | tCO2e | |||||||||||||||||||||
40 | |||||||||||||||||||||||||
41 | Project Leakage | ||||||||||||||||||||||||
42 | Because stockpiled ODS in Ghana is not sold or re-used in Ghana, the destruction of ODS in this Project will not lead to the production or consumption of other refrigerant chemicals, and therefore no substitute refrigerant emissions will be calculated. | 0 | 0 | tCO2e | |||||||||||||||||||||
43 | |||||||||||||||||||||||||
44 | Estimated net GHG emission reductions or removals | ||||||||||||||||||||||||
45 | Difference between avoided ODS emissions & project emissions | 19,632.28 | 135,837.10 | tCO2 | |||||||||||||||||||||
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