
Getting to 2050: Canada's Transition to a Low-emission Future — Advice for Long-term Reductions of Greenhouse Gases and Air Pollutants
Air pollutants, including VOCs, SOx, NOx, and PM [29] (individually or in combination as smog and acid rain) have been shown to cause adverse health and environmental effects. Scientific evidence indicates a strong correlation between ambient air concentrations of the pollutants and significantly adverse effects on human health, ranging from respiratory conditions such as asthma and chronic bronchitis to premature death and increased mortality. From an environmental perspective, smog has been linked to reduced plant productivity resulting in reduced agricultural crop yields and forest growth. Acid rain and acid deposition from SOx and NOx emissions also present a well-known threat to ecosystems, notably lakes and forests.
The NRTEE looked at potential long-term (2050) national emission reduction targets for a number of air pollutants including SOx, NOx, VOCs and PM. Specifically, we assessed potential emission reductions of 50% and 80% below current levels. We also looked at an integrated approach whereby significant GHG and air pollutant emission reductions could be addressed in the same time frame (using a 65% GHG reduction target and 50% reduction targets for the air pollutants). The goal of this integrated analysis was to assess the integrated effects between the pricing pathways for the two GHG targets while incorporating any co-benefits and integrated effects of the shallow prices for the air pollutants. We explored to what extent we could take advantage of the co-reductions to reduce the GHG prices and still meet a 65% GHG reduction target.
The following section first discusses the findings of the air pollutant analysis, followed by a discussion of the conclusions of an integrated approach.
Air Pollutant Reductions
As with GHG emissions, anthropogenic air pollutant emissions result primarily from fossil fuel combustion. However, air pollutant emissions differ in three important ways. First, they have the greatest effect in the local area around the emissions' source. Second, most air pollutants have a fairly short residence period in the atmosphere, so impacts can vary significantly over time. Finally, while combustion-based GHG emissions can be linked closely to the amount of fossil fuel combusted, combustion-based air pollutant emissions can vary greatly depending on conditions by sector, fuel quality and end-of-pipe emission controls. As a result of these differences the forecasts generated in the modelling undertaken for the NRTEE should be considered indicators of overall trends, rather than precise values.[30]
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
Based
on our research into potential air pollutant reductions
the NRTEE makes the following observations:
The research suggests that the sectoral implications of significant, long-term emission reductions are not uniformly distributed. The transportation sector is responsible for a large portion of the reductions of NOx, PM10 and VOC emissions. However, these reductions are largely the result of regulations set to be implemented in the near future, and therefore will occur regardless of (and not because of) the emissions prices.
The allocation of the remaining emissions reductions is highly dependent upon the air pollutant in question. In general, the sectors that contribute the most to reductions had high emission rates in 2005 and lower marginal costs of abatement. For example, reductions in SOx emissions are highly concentrated in the electricity generation sector, which contributes 26% of the 2005 levels assumed in the model, and has a relatively low marginal cost of abatement. In some sectors, the emissions price is insufficient to cause a reduction in emissions from 2005 to 2050. For example, the petroleum crude extraction industry experiences an increase in SOx emissions from 2005 to 2050 when the national -50% price is implemented, simply because overall activity increases almost five-fold. In these cases, the emissions price is not large enough to offset the emission effects of increased output from the sector.
An Integrated Approach
Industrial emissions of GHGs and air pollutants each account for approximately 50% of Canada's total air emissions and share many common sources. Therefore it makes sense to explore the possibility of addressing both sources in an integrated regulatory approach.
The first finding of this assessment is that an integrated approach lowers the prices associated with emission reductions. Specifically, the research shows that the GHG price necessary to hit the -65% target is significantly lower when implemented along with air pollutant prices, than when the GHG price is implemented alone (Figure 8). The air pollutant prices encourage investment in higher efficiency and lower emissions technologies and processes, and therefore the GHG prices do not have to be as strong to hit the target. This finding confirms that the GHG co-pollutant reduction experienced with air pollutant pricing effectively reduces the final GHG price needed to reach the target.
Many actions that reduce GHG emissions also reduce air pollutant emissions. For example, climate change policies focused on improved energy efficiency also will lower air pollutants associated with producing energy, thereby improving local air quality. The use of CCS eliminates most SOx and PM emissions associated with combustion. Fuel switching from coal to natural gas will decrease air pollutant emissions. Similarly, policies targeting air pollutants, especially SOx, encourage fuel switching from relatively sulphur-intense (and GHG-intense) coal to less sulphur-intense (and GHG-intense) natural gas and electricity.
Figure 8: Comparison between the GHG prices required to reach the -65% GHG target when the GHG price is implemented alone, or in conjunction with air pollutant prices

The second key finding of this analysis was that an integrated approach will likely result in co-benefits related to air pollutant reductions. For example, our research shows that the SOx price that attains a 50% reduction when implemented alone triggers a reduction of 83% when implemented in conjunction with the GHG and other air pollutant emissions charges.
In conclusion, the NRTEE research suggests that there are significant opportunities to reduce GHG and air pollutant emissions in an integrated approach. The application of relatively inexpensive air pollutant emission reduction actions, induced by emissions pricing, may significantly reduce the GHG emission price necessary to achieve deep targets, while reaping the co-benefits of lower local air pollution.
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