XXI
Figure ES.5: The range of estimated potential emission reductions in various NSA studies.
Figure ES.5a: Emission reduction potential of pledged commitments by NSAs.
70 Individual commitments 0.53 60 0.46 50 1.85 0.02 0.45 0.55 3.7 3.7 8 40 19 Ranges
Scaled up potential based on assumptions
40 2ºC scenario Single Initiatives 0.4 0.74 1.40 5.5
59 56
Current policy scenario
Unconditional NDC scenario
Multiple Initiatives 65
No policy baseline
Figure ES.5b: Scaled up potential emission reductions based on single and multiple initiatives.
* Data-Driven Yale, NewClimate Institute, and PBL Netherlands
Source: Based on data in table 5.2. Note: a) For studies that include ranges, median estimates are provided with ranges indicated in fi gures ES.5a and ES.5b. b) Studies that are cross-hatched evaluate single and multiple ICI goals rather than individual actors’ recorded and quantifi ed pledges. They rely on assumptions of future scaled-up impact and therefore represent potential rather than a quantifi ed analysis of individual actors’ NSA pledges. c) Extrapolation of 2025 estimates has been made.
compared with current policy. A more comprehensive assessment of all non-state and subnational climate action occurring globally is limited by the current low level of available data and lack of consistent reporting on non-state and subnational climate action.
compared with full unconditional NDC implementation, and up to 1.85 GtCO2
e/year (range 0.2–0.7 GtCO2 e/year (range 1.5–2.2 GtCO2
Non-state actors need to adopt common principles when formulating their actions. Such principles should include clear and quantifi able targets based on relevant benchmarks, technical capacity of the actors, availability of fi nancial incentives and the presence of regulatory support.
6. Fiscal policy reform can play a key role in creating strong incentives for low-carbon investments and reducing GHG emissions. Revenues from carbon
However, the additional emission reductions under full implementation of pledged commitments made so far by individual non-state actors are still quite limited: up to 0.45 GtCO2
e/year) by 2030 e/year)
pricing can be used for reducing other taxes, increase spending on social issues or compensating low-income households. Well-designed fi scal reform packages can reduce the costs of mitigating emissions, thereby making these fi scal reforms more socially acceptable. The use of carbon pricing to reduce GHG emissions is still only emerging in many countries and generally not applied at a suffi cient level to facilitate a real shift towards low- carbon societies.
Fiscal policy is a key government tool for managing and infl uencing the national economy and can be used to tax fossil fuels or subsidize low-emission alternatives as a way of infl uencing carbon emissions and ultimately investments in the energy sector.
Pricing of carbon emissions through taxes or domestic emissions trading systems is, in many countries, part of the national climate policy and is referenced in many NDCs as one of the possible policy tools to be used. Before 2005, when the Kyoto Protocol entered into force, hardly any emissions were covered by carbon taxes or
Annual GHG emissions in 2030 (GtCO2e)
America's Pledge (2018)
Kuramochi et al. (2017) Yale-NCI-PBL* (2018) 1a
Yale-NCI-PBL* (2018) 1b Roelfsema (2017)
Arup and C40 Cities (2014)
Global Covenant of Mayors (2018) Compact of Mayors (2015)
The Climate Group (2017)
Erickson and Tempest (2014) Roelfsema et al. (2018)
CDP and WeMeanBusiness (2016)
Graichen et al. (2017) Yale-NCI-PBL* (2018)
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