The Economics of Climate Change

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Presentation transcript:

The Economics of Climate Change Lecture 9: Credit-based Mechanisms Dr. Markus Ohndorf Autumn Term 2014

Previous lectures Discussion of Price- and Quantity Mechanisms Can be first-best efficient Require commitment of participating countries What about countries that do not want to commit, but have a high potential for low-cost reductions? Developing countries

Remember the Kyoto World?

MAC curve for the whole non-Annex I region Source: ECN (2010)

Findings of ECN study back in 2010 Total identified GHG reduction potential in 2010 in the non-Annex I region as a whole amounts to 2.1 GtCO2 equivalent Most reduction potential (62 per cent) in the power sector (energy efficiency, fuel switch) and demand side energy efficiency measures Approximately 1.9 GtCO2 eq. is feasible at costs of up to US$ 4 per tCO2eq reduction Large fraction of identified potential can be realized in a limited number of non-Annex I countries. Most reduction potential has been identified in China and India (some 60 per cent)

Credit-based Mechanisms Best known: Clean Development Mechanism (CDM) and JI. CDM: Financing GHG reduction or sink projects in developing countries, i.e. outside of Annex B countries of the Kyoto Framework CDM certificates (Certified Emission Reductions, CERs) are in principle fully fungible with AAUs (Assigned Amount Units from inter-country emissions trading). Due to this fungibility, certificates also feed into other cap-and-trade systems, like the EU ETS. Hence, non-additional certificates from credit-based schemes also affect the environmental effectiveness of cap-and-trade schemes Monitoring is not only to maximize emission reductions, but also minimize overreporting

The Clean Development Mechanism

Technology transfer via the CDM

The Problem of „Cheating“ within the CDM A credit-based emissions trading system without exogenously set targets is subject to information asymmetries, which are more severe than within a cap-and-trade system The Project Developer has better information than the regulator Problematic, because the good traded on the market is entirely created by regulation Control Costs are considerably high.

Verification and Monitoring within the CDM Due to the lack of targets the seller and the buyer have an incentive to misreport either the baseline or actual emissions, or both. The CDM regulation is based on third-party verification by a so-called “Designated Operating Entity” (DOE). The DOE being remunerated by the project parties has, in principle, an incentive to collude. (Difference to other verification markets) The regulator (CDM Executive Board) needs to reduce the incentives to cheat within the market. The current main measure of enforcement are spot-checks. The budget to execute spot-checks is limited. Control through spot-checks

Discussion The CDM has been severely criticized. What is your assessment on the efficiency of such mechanisms? What are the alternatives? How would you design an alternative approach?

Incomplete enforcement Model Setup

Information asymmetry over costs  

Optimization problem of the Regulator:

Optimal response of project developer

Characteristics of the optimal Monitoring Strategy

Conclusions There are significant differences compared to optimal monitoring for a tax regime: With a large enough share of projects with high abatement costs, the regulator has an incentive to induce full compliance for these cost types over the whole range of verifiability where this is possible. With decreasing verifiability, the optimal audit pressure features a ‘jump’ downwards when reaching levels of verifiability, for which the regulator cannot deter overreporting by high-cost projects. For projects with intermediate verifiability, optimal monitoring pressure can be either non-increasing or ‘U-shaped’, depending on the relative stringency of the penalty schedule. The most cost effective way to prevent misreporting is to set high standards for project admission with respect to verifiability.

Current market prices for CERs Spot price as of November 18th: 0.42 €/t Reason for price drop: Low demand meets oversupply EU ETS will in the future accept only CERs from LDCs Other potentially large buyers refrain from joining the KP