Abstract

This paper finds that it is optimal to start a long-term emission-reduction strategy with significant short-term abatement investment, even if the optimal carbon price starts low and grows progressively over time. Moreover, optimal marginal abatement investment costs differ across sectors of the economy. It may be preferable to spend $25 to avoid the marginal ton of carbon in a sector where abatement capital is expensive, such as public transportation, or in a sector with large abatement potential, such as the power sector, than $15 for the marginal ton in a sector with lower cost or lower abatement potential. The reason, distinct from learning spillovers, is that reducing greenhouse gas emissions requires investment in long-lived abatement capital such as clean power plants or public transport infrastructure. The value of abatement investment comes from avoided emissions, but also from the value of abatement capital in the future. The optimal levelized cost of conserved carbon can thus be higher than the optimal carbon price. It is higher in sectors with higher investment needs: those where abatement capital is more expensive or sectors with larger abatement potential. We compare our approach to the traditional abatement-cost-curve model and discuss implications for policy design.

Highlights

  • This paper finds that it is optimal to start a long-term emission-reduction strategy with significant short-term abatement investment, even if the optimal carbon price starts low and grows progressively over time

  • Once all the buildings are energy neutral, no more greenhouse gas (GHG) can be saved in the building sector; and if every coal power plant is replaced with renewable power, the abatement potential of the power sector is depleted

  • Optimal marginal abatement investment costs, expressed in dollars invested per discounted abated ton of carbon, can be higher than the carbon price

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Summary

Optimal timing of abatement investment

We start the resolution of problem 6 from the steady state. The cumulative emission ceiling B is reached at an endogenous date T. The exponentially-increasing carbon price is reminiscent of an Hotelling rule It ensures that the present value of the carbon price is constant along the optimal path until full decarbonization, such that the social planner (or the market) is indifferent between one unit of abatement at any two dates.. Before T, emissions are strictly positive, abatement capital is lower than its potential at < εref , and optimal investment dynamics are described by the first order condition (Appendix A) :. Equation (9) means that if there was a well-functioning market for abatement capital, the rental cost of abatement capital would be equal to the carbon price. The strictly decreasing profile happens for stringent climate targets, that is for high carbon prices compared to abatement investment costs μ ≫ (r + δ) c′ (δεref ) (see Fig. 1). Lecocq and Shalizi (2014) report bellshaped investment pathways in the case of the transition to nuclear power in France and the building of the national interstate highways in the United States

Optimal cost of abatement investment
Optimal sectoral allocation of abatement investment
Specification and calibration
Results
Conclusion
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