
Getting to 2050: Canada's Transition to a Low-emission Future — Advice for Long-term Reductions of Greenhouse Gases and Air Pollutants
The apparently small impacts on national economic performance under a broad-based carbon price mask regional and sector implications that may be of greater concern. Understanding the real or perceived distribution of impacts on regions and sectors is important since it tends to drive climate change policy in Canada. Where real income or employment effects are forecasted, the appropriate climate change policy response is to maintain the carbon “signal” and design complementary income and employment policies to smooth the transition and minimize dislocation. With this in mind, the following discussion explores regional abatement efforts, sectoral price and output effects, and costs to consumers. Again, the NRTEE recognizes the uncertainty inherent in our analysis, and therefore the following should be viewed as directional at best. Regional abatement effort could ultimately be uniform but will differ in time:
Executive Summary
1 Introduction
1.1 Purpose
1.1.1 Clean Air Act Reference and NRTEE’s Advice
1.1.2 Federal Regulatory Framework and NRTEE’s Reference
1.1.3 Conceptual Framework
1.2 Important Context and Assumptions of the NRTEE’s Greenhouse Gas Advice
1.3 Transition to 2050
2 Managing the Transition to a Low-emission Future
2.1 Enabling Conditions for Managing the Transition
2.1.1 A Note on Our Modelling, Assumptions and Caveats
2.1.2 Canada Acting in Concert with the World
2.1.3 Policy Certainty Beyond the Short Term is Central
2.1.4 An Economy-wide Emission Price with Complementary Policies
2.1.5 Technology Deployment Will Be Imperative
2.1.6 Air Pollutant Reductions and an Integrated Approach
2.2 Understanding the Economic Risk and Uncertainties of the Transition
2.2.1 Long-term National Economic Growth Prospects
2.2.2 Regional and Sectoral Outcomes
2.2.3 The Importance of the Enabling Conditions
3 Key Findings and Recommendations
4 Looking Ahead
5 Appendix
5.1 Letter of Reference from the Minister of Environment
5.2 NRTEE Approach to the Reference
5.3 Glossary
5.4 Research Commissioned by the NRTEE in Support of the Reference
5.5 Key Attributes of the Energy Economy Model – CIMS
5.6 Messages from Regional Meetings Across Canada
5.7 Meeting Participants – NRTEE’s Research on
Clean Air and Climate Change - 2007
Figure 10: Provincial GHG emission reduction effort for 20%/65% share of national reductions and below regional baseline
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Sectoral abatement effort will likely not be uniform over time with some acting earlier than others. Notably, the industrial and energy supply sectors would likely provide more emission reductions by 2020, but in 2050 there could more or less be a convergence as the residential, transportation and commercial sectors catch up in response to the higher emission prices. Figure 11 provides the distribution in time of abatement effort by sector. The different responses of the sectors in terms of timing and magnitude point to the need for a flexible climate change policy signal, such as the emission price we have advocated in this Advisory Report.
Figure 11: Sectoral Abatement Effort
| 2020 | 2050 | |
| Canada | -20% | -65% |
| Residential | -15% | -70% |
| Commercial/Institutional | -13% | -64% |
| Transportation | -7% | -61% |
| Total Industrial | -17% | -64% |
| Chemical Products | -13% | -67% |
| Industrial Minerals | -36% | -75% |
| Iron and Steel | -6% | -54% |
| Non-Ferrous Metal Smelting | -5% | -49% |
| Metals and Mineral Mining | -9% | -37% |
| Other Manufacturing | -14% | -66% |
| Pulp and Paper | -32% | -71% |
| Energy Supply | -26% | -68% |
| Coal Mining | -3% | -13% |
| Electricity Generation | -23% | -72% |
| Natural Gas Extraction | -10% | -33% |
| Petroleum Crude Extraction | -41% | -69% |
| Petroleum Refining | -14% | -75% |
Sectoral profitability impacts and possible economic dislocations seem plausible under either a 45% or 65% reduction scenario, even when we assume that the world (and especially the United States) acts in concert to reduce GHG emissions. The extent to which domestic firm output may further decline and profitability effects intensify will be a function of how much product prices rise relative to international competitors. The logic of this assertion is straightforward and starts with the impact of the emission price on product prices. In domestic markets with little international competition, Canadian firms face the same emissions price with impacts differentiated by the relative abatement costs and emission intensities, where higher carbon-intensity firms face higher costs and possibly lower market shares. In this case, the major determinant of the profitability or economic impact will be any reduced demand for the product, for example a reduction in national coal demand as identified in Figure 12 below. For sectors exposed to international competition, either in domestic or international markets, the impact will be more strongly linked to relative emission prices between countries. If all countries more or less act in concert on emission pricing, competitiveness impacts largely disappear. But if countries do not move in concert and Canada imposes deep limits on emissions, there will be more pronounced competitiveness impacts leading to profitability reductions.
Figure 12: Impacts on production costs and output
| Changes in Production Costs Relative to the BAU | Changes in Output Relative to the BAU | |||
| 2020 | 2050 | 2020 | 2050 | |
| Residential | 6% | 1% | -8% | -5% |
| Commercial/Institutional | 1% | 1% | -2% | -2% |
| Transportation | 8% | 1% | -6% | -5% |
| Industrial | ||||
| Chemical Products | 17% | 15% | -6% | -5% |
| Industrial Minerals | 24% | 20% | -49% | -50% |
| Iron and Steel | 9% | 13% | -3% | -4% |
| Non-Ferrous Metal Smelting | 7% | 7% | -3% | -2% |
| Metals and Mineral Mining | 3% | 6% | -2% | -7% |
| Other Manufacturing | 5% | 5% | -1% | -1% |
| Pulp and Paper | 2% | 2% | -6% | -2% |
| Energy Supply | ||||
| Coal Mining | 25% | 93% | -6% | -20% |
| Electricity Generation | 31% | 24% | 6% | 35% |
| Natural Gas Extraction | 19% | 39% | -4% | -9% |
| Petroleum Crude Extraction | 30% | 34% | -3% | -5% |
| Petroleum Refining | 6% | 6% | -12% | -50% |
Figure 12 traces out some of the possible price and output outcomes under our scenario where Canada acts with the industrialized world on deep reductions. With emission pricing under this scenario, we would expect the domestic energy system to move toward less carbon intensive energy sources. This is indeed observed in our modelling with significant growth in low-emitting sources of electricity (+40% from business-as-usual projections) and large reductions in carbon-intensive refined petroleum products (-50%) and coal (-20%). Figure 13 presents the associated fuel supply and demand under a long-term 65% reduction scenario. The output of oil and gas remains more or less unaffected in our scenario reflecting the observation that continued global demand for oil will drive energy exports, even under global emission constraints and rising domestic production costs. If coal and petroleum product exports follow this possibility, the output declines we observe in Figure 13 could be reduced. That said, there would then be the associated issue of rising global emissions (or leakage) with more Canadian energy exports.
The reduction in output from industrial sectors, either in response to higher energy prices or as an abatement option, could be small on aggregate. Our modelling suggests decreases in the order of 3% below forecast levels in 2020 and 4% in 2050. Some sectors, like pulp and paper, may invest earlier and experience transitional output reductions that are largely reduced over time. Other sectors such as metals and mineral mining may make investments later in response to higher emission prices. The one exception to this story of a low overall output effect is industrial minerals, which primarily includes cement. This sector could experience large output reductions due to high abatement costs that raise product prices significantly (i.e., 30%), thereby reducing demand. For the most part, the provincial and national stocks of housing remain stable, with some medium-term reductions in 2020 but a return to BAU forecasts by 2050. The quantity of commercial buildings and the transport sector remain unaffected in terms of size but instead would need to lower their carbon intensity considerably.
Figure 13: Change in energy mix by sector
| Residential | Transportation | ||||
| 2020 | 2050 | 2020 | 2050 | ||
| Natural Gas | -4% | -6% | RPPs | -1% | -57% |
| RPPs* | -5% | -28% | Electricity | 0% | 11% |
| Electricity | 9% | 35% | Hydrogen | 0% | 5% |
| Wood | 0% | 0% | Renewable | 0% | 40% |
| Industrial | Electricity | ||||
| 2020 | 2050 | 2020 | 2050 | ||
| Natural Gas | -3% | -6% | Natural Gas | 4% | 8% |
| Coal | 0% | -1% | Coal | -11% | -29% |
| RPPs | -6% | -19% | RPPs | 0% | -2% |
| Electricity | 4% | 18% | Renewable | 7% | 23% |
| Wood | 5% | 7% | |||
*Refined Petroleum ProductsFor the average household, price effects can be expected, with both “pain” and “gain” associated with deep GHG reductions. But these price effects are likely not outside the ongoing energy price swings we have experienced, and thus increased energy costs for households are probably important but not significant: