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The Government of Canada has published the long-awaited framework (the Framework) for an oil and gas sector emissions cap. If implemented, the proposed cap-and-trade system would limit 2030 emissions from covered sources in the sector to 20-23% below 2019 levels (or 35-38% below 2019 levels, without the use of compliance flexibility).
Prime Minister Trudeau promised an emissions cap for the oil and gas sector during the 2021 election campaign. Since then, the Government of Canada has taken several key steps in developing the Framework:
The proposed cap would function, in many ways, like a typical cap-and-trade system: a cap would be set on emissions from the oil and gas sector and allowances (essentially, licences to emit a tonne of carbon dioxide equivalent, or CO2e) equal to the cap would be allocated to covered facilities within the sector. Those allowances could be traded between covered facilities, which, in theory, incentivizes emissions reductions at facilities with the lowest marginal cost of abatement. Over the course of each compliance period, facilities would need to either retire allowances equal to their emissions during that period or “true up” any shortfall in allowances by purchasing and retiring other eligible compliance instruments, subject to certain limits.
In a typical cap-and-trade system, the cap would contract over time, making allowances scarcer and thereby increasing demand for allowances and other compliance instruments. This, in turn, would increase the cost of each tonne of CO2e and incentivize investments in more costly abatement measures at covered facilities. The Framework does not outline how the size of the cap would change after 2030 and only mentions that the post-2030 period will need to balance regulatory certainty with the challenges associated with projecting future conditions.
According to the Framework, the cap-and-trade system would have the following design features.
The cap would cover emissions from LNG and upstream oil and gas facilities, including conventional oil, offshore, oil sands, and natural gas production and processing facilities1. Upstream facilities represented 85% of sector emissions in 2021, and new LNG facilities are projected to be a growing source of emissions.
The Framework does not specify an annual emissions threshold below which facilities in the covered sectors would be exempt from compliance. In contrast, the cap-and-trade systems of California and Québec, which are linked under the Western Climate Initiative (WCI), only require the participation of facilities with annual emissions above 25 kilotonnes (kt). Currently, Environment and Climate Change Canada only requires annual emissions reporting from facilities with emissions exceeding 10 kt per year of CO2e. However, the Framework notes that the upstream oil and gas sector includes many smaller emitters with annual emissions below 10 kt per year. While these facilities are not major emitters on their own, collectively they are estimated to account for one-third of the sector’s total GHG emissions. Therefore, the Framework states that the government is examining provincial approaches to covering smaller emitters to support an efficient approach to covering them under the federal cap-and-trade system.
The proposed cap would cover direct GHG emissions from covered facilities. However, the cap-and-trade system would also take into account transfers of thermal energy, hydrogen carbon dioxide (CO2), and electricity to and from these facilities. In particular, each covered facility would be required to report and quantify information related to the purchase and sale, production, use and import, and export from the facility of thermal energy, hydrogen and electricity, as well as CO2 transfers for storage. According to the Framework, this accounting would help ensure a level playing field and minimize leakage risk—in particular, by minimizing the incentive for covered facilities to relocate energy production (and any associated emissions) outside of the cap. That said, the Framework contains little detail on how this accounting would occur and how transfers of energy and CO2 would impact facility emissions subject to the cap.
Beginning in 2030, the Government of Canada would issue allowances to covered facilities equal to the initial emissions cap. There would also be a separate ceiling on the emissions the entire sector would be allowed to emit in a year. That ceiling—what the Framework calls the “legal upper bound”—would be equal to the emission cap (i.e., the amount of allowances distributed in a year) plus the maximum allowable amount of other compliance instruments that could be used in such year. Based on current estimates, the initial 2030 emissions cap would be between 106 to 112 MT. There would also be about 25 MT in additional compliance flexibility, meaning that the legal upper bound would be around 131 to 137 MT. According to the Framework, the final emissions cap and legal upper bound would be set based on the best information available when the regulations are finalized. As mentioned above, the Framework does not outline how the cap or the legal upper bound will change in the post-2030 period. However, it does mention that the legal upper bound would decrease over time to ensure that the covered sources achieve net-zero GHG emissions by 2050.
Allowances would initially be allocated to covered facilities free of charge. However, the Framework suggests that allowance auctions may be considered for future compliance periods. Allowance auctions are a prominent feature in other cap-and-trade systems; for example, the WCI has held quarterly allowance auctions for years.
According to the Framework, in allocating allowances to covered sources, the Government would recognize better performers that are able to produce the same or similar products with a lower emission intensity. The Framework does not provide any details on how this emissions intensity-based allocation method would work in practice. Rather, the government is seeking feedback on the approach.
The cap-and-trade system would use three-year compliance periods, thereby helping to smooth the impact of any emissions volatility at covered facilities. The multi-year compliance periods would have both an annual compliance requirement and a final true-up at the end of each compliance period. For example, in each of the first and second years of a compliance period, facilities would be required to remit compliance instruments covering up to 30% of their verified GHG emissions, less any GHG emissions permanently stored, for the year.
If a facility was not able to cover its emissions with the allowances allocated to it, it could buy and retire allowances from other facilities who have a surplus. A facility could also use certain other compliance instruments to cover its emissions, subject to certain limits:
Facilities would be able to bank any unused allowances for up to two compliance periods (six years). This would apply to allowances allocated to the facility or purchased from another facility. The Government of Canada is considering whether there should be a limit on the total number of allowances that can be banked.
Given its purpose to solicit initial feedback on the proposed cap-and-trade system, the Framework, not surprisingly, leaves certain other issues unaddressed:
The Government of Canada plans to publish final regulations in 2025, with the first reporting obligations starting as early as 2026 and full system requirements phased in between 2026 and 2030.
The proposal is open for public comments until February 5, 2024, and the Government of Canada plans to publish draft regulations in mid-2024. Comments may be submitted to [email protected]. As always, please feel free to contact members of Torys’ Climate Change Practice regarding the Framework or any planned submissions on the proposed cap-and-trade system.
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