Prices and Quantities in a Climate Policy Setting Svante Mandell.

Slides:



Advertisements
Similar presentations
Support of renewable energy: Prices versus quantities GIN 2006, Cardiff Jeroen De Paepe University of Ghent.
Advertisements

Product Market Competition, Insider Trading Regulation, and Optimal Managerial Contracts Chyi-Mei Chen Chien-Shan Han.
1 Chapter 14 Practice Quiz Environmental Economics.
Moving toward Stringency in Emissions Trading Professor Lesley McAllister University of San Diego School of Law.
Environmental economics Chapter issues what is appropriate level of waste? how to achieve that level (who has to reduce how much?)
In chapter 10, we look for the answers to these questions:
Pollution Policy with Imperfect Information (Ch. 8)
International Emission Policy with Lobbying and Technological Change Tapio Palokangas Presentation for the students March 18, 2009.
Climate Change 1. What is climate change? IPCC: A change in the state of the climate that can be identified by changes in the mean and/or the variability.
Lecture Presentation Software to accompany Investment Analysis and Portfolio Management Seventh Edition by Frank K. Reilly & Keith C. Brown Chapter.
Managerial Economics: Lecture 5 Carlos A. Ulibarri Department of Management New Mexico Tech.
Free Trade and Strategic Environmental Policy Huei-Chin Lin National Dong-Hwa University.
Who Wants to be an Economist? Part II Disclaimer: questions in the exam will not have this kind of multiple choice format. The type of exercises in the.
Monopoly While a competitive firm is a price taker, a monopoly firm is a price maker. A firm is considered a monopoly if it is the sole seller of.
Economic Issues in Climate Change Kathleen Segerson Department of Economics University of Connecticut.
International Energy Workshop June, Paris Gernot Klepper & Sonja Peterson Kiel Institute for World Economics The EU Emissions Trading Scheme Efficient.
Emissions Trading (Cap and Trade) Kate Macauley. 1. Economics of emissions trading 2. Overview of the EU Emissions Trading Scheme (ETS)
Interjurisdictional Tax Competition, Voting and Environmental Policy Oates, Wallace and Robert M. Schwab “Economic competition among jurisdictions:
Dual discounting in forest sector climate change mitigation Hanne K. Sjølie Greg Latta Birger Solberg Forest sector modeling workshop Nancy,
Chapter 9 Externalities: When Prices Send the Wrong Signals
C. Bordoy UWC Maastricht Market Failure Evaluation of policies to correct externalities.
Operations Management
Environmental Economics Class 7. Incentive Based Regulation: Basic Concepts Up to this point, the focus has been on resource allocation. Since the use.
Stiftelsen Frischsenteret for samfunnsøkonomisk forskning Ragnar Frisch Centre for Economic Research Climate Agreements and Technology.
Exam 3 review. optimal pollution what is appropriate level of waste? how to achieve that level (who has to reduce how much?) identify efficient levels.
Copyright©2004 South-Western Monopoly. Copyright © 2004 South-Western While a competitive firm is a price taker, a monopoly firm is a price maker.
Lecture Presentation Software to accompany Investment Analysis and Portfolio Management Seventh Edition by Frank K. Reilly & Keith C. Brown Chapter 7.
Limiting Green House Gas emissions: an economist’s perspective
Some Background Assumptions Markowitz Portfolio Theory
Pollution control: instruments
Market Mechanisms to Curb Greenhouse Gases: Challenges and Future Directions Joe Kruger February 20, 2007 Joe Kruger February 20, 2007.
Cap and Trade 101 Marlon G. Boarnet Professor of Public Policy Director of Graduate Programs in Urban Planning and Development University of Southern California.
Energy Forum Compensation arrangements for indirect EU ETS cost effects Presented by Vianney Schyns Brussels 9 June
Chapter 2 Externalities and the Environment McGraw-Hill/Irwin
Aim: What can the government do to bring stability to the economy?
Environmental Economics Week 2 MARKET FAILURE AND ENVIRONMENTAL ECONOMICS READING: Common: Chapter 4 Perman et al: Chapter 5 and 6.
Externalities.
ECON International Economics Chapter 5 Protectionism and Free Trade.
Investment Analysis and Portfolio Management First Canadian Edition By Reilly, Brown, Hedges, Chang 6.
Dr. Laura Dawson Ullrich March 25, Q per year $ MB MD MPC MSC = MPC + MD Q1Q1 Q* Actual output Socially efficient output b a c.
Profit has a deep impact on the present, future of an enterprise. It is also a supreme motive of the enterprise. It is a process of determining profits,
Bruce Ian Carlin, Miguel Sousa Lobo, S. Viswanathan: Episodic Liquidity Crises: Cooperative and Predatory Trading (The Journal of Finance, 2007) Presented.
Notes for Chapter 5 ECON Economics of Environmental Quality The exchange of private goods and services will generally result in socially efficient.
Copyright © 2008 Pearson Addison-Wesley. All rights reserved. Chapter 17 The Economics of Environmental Protection.
1 Managing Flow Variability: Safety Inventory Operations Management Session 23: Newsvendor Model.
Allocation of CO 2 Emission Allowances in RGGI Dallas Burtraw, Karen Palmer, Danny Kahn Resources for the Future Presentation to RGGI Stakeholder Meeting.
Chapter 22. The limits to stabilization policy: Credibility and uncertainty ECON320 Prof Mike Kennedy.
Copyright©2004 South-Western 15 Monopoly. Copyright © 2004 South-Western Monopoly While a competitive firm is a price taker, a monopoly firm is a price.
Key challenges and possible new formats for CDM post-2012 ECBI Fellowships, Oxford, Sep. 3, 2007 Axel Michaelowa,
CRAIG PIRRONG JANUARY, 2009 Efficient Carbon Policy: Taxes vs. Cap & Trade.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 13 Economics of Pollution Control: An Overview.
Business in a Modern World Fabian Girod Business in a Modern World 1 Markets, Firms, and the Role of Governments Legal systems; externalities and public.
Resolving Different Levels of Stringency  As framed: –There are benefits to linking separate “cap-and- trade systems.” –There may be “weak” and “stringent”
The effect of over-allocation and price uncertainty on investments under the EU ETS Frank Venmans | Université de Mons | Grantham Institute-LSE Frank Venmans.
Policy Tools: Correcting Market Failures. What are the most serious problems we face? Climate change Agricultural production Peak oil Water supply Biodiversity.
Externalities 1. Externality –The uncompensated impact of one person’s actions on the well-being of a bystander –Market failure Negative externality –Impact.
Environmental policy with uncertainty/imperfect information Price or quantity? M Weitzman, 1974, Prices vs quantities, RevEconstudies.
An Intro to the Economics of Climate Policy
Economics of Pollution Control: An Overview
The Economics of Climate Change
C h a p t e r 3 EXTERNALITIES AND GOVERNMENT POLICY
Shaping Greenhouse Gas Abatement Strategies
Environmental and Natural Resource Economics
Chapter 2 Externalities and the Environment McGraw-Hill/Irwin
Environmental and Natural Resource Economics 3rd ed. Jonathan M
Economics of Pollution Control: An Overview
Regional Climate Alliances Spring 2008
Andy Reisinger1 Keywan Riahi2 Oscar van Vliet2
Approaches for Future International Co-operation
Presentation transcript:

Prices and Quantities in a Climate Policy Setting Svante Mandell

Observations and aim In practice (the EU): ● Overarching quantitative target for CO 2 ● A dual regulation; CaT and emission taxes Under uncertainty, emissions taxes outperform CaT for handling GHG Q: (When) is a dual regulation justifiable?

The model Starts in a classic Weitzman (-74) setting ● Linear MAC- and MAB-functions ● Uncertainty (additative, symmetric round zero) ● Aggregate abatement benefits relevant Answers if CaT or emission tax is preferable CO 2 causes a stock externality  A flat MAB  Variation in emissions ‘better’ than variation in price  Use a tax

The model, cont. Mandell (2008), JEEM: Allow for dual regulation ● Tax a subset of emitters, the rest CaT Outcome closer to optimum, but not cost effective Full CaT never optimal, full tax optimal for (sufficiently) flat MAB-functions

The model, cont. This paper: ● Flat (horizontal) MAB-function ● A global cap that may never be exceeded ● Two periods Intuition: ● The global cap may require high tax to be met  full tax may not be optimal

Timing of the model STAGE 0 Policy maker decides on share to tax and tax level STAGE 1 Emitters choose emission volumes Uncertainty 1 is resolvedPossible surplus is bankedUncertainty 2 is resolved STAGE 2 Emitters choose emission volumes Tax level may be changed

Policy goal Policy maker strives to ● Minimize present value of expected efficiency loss ● S.t. the global cap must not be exceeded Thus, we need an expression for E{DWL tot }

Two sources of eff. loss Volume error Actual emissions differ from efficient amount Allocation error Abatement efforts not distributed in a cost effective manner Period 1 Period 2

The taxes As low as global cap permits, but never below the MAB Less stringent global cap  lower taxes Period 1 is ”sunk” when setting T 2 ● T 2 typically lower than T 1, due to surplus Taxes increase in share of taxed emitters

 n * / N  = 0  = 0.5  = 1 ”Strict” global caps, i.e., a cap below expected efficient level Optimal share to tax (n*) ”Lenient” global caps, i.e., a cap above expected efficient level  = discount factor At  =0 the model becomes a one-period model (outcomes in period 2 are given zero weight)

Some intuition for n* Start in a situation where ● Global cap = expected efficient level ● All emitters are in CaT At low MAC realizations – too high emissions At high MAC realizations – too low ● Thus, an expected volume error ● But no allocation error

Some intuition for n* (cont.) Move some emitters to taxed sector ● At low realizations; decreased error ● At highest realization; emissions equal global cap ● Other high realizations; increased error ● And also an allocation error Motivates a small taxed sector

Some intuition for n* (cont.) Now, consider a higher global cap A larger set of realizations will yield a decrease in efficiency loss Motivates taxing a larger share Thus, n* increases in the global cap

The role of the discount factor Most likely a surplus in period 1 ● Policy maker may not destroy permits – increased cap period 2 Lenient cap period 1  even more so period 2  risk for large efficiency loss Stringent cap period 1  less stringent period 2  may decrease efficiency loss

The role of the discount factor  n * / N  = 0  = 0.5  = 1 More weight on period 2 calls for a lower n* under leninet global cap… …but a higher n* under stricter global cap

Conclusions Often, a dual regime is better than full emissions tax or CaT Even accounting for not cost effective This depends on ● The global cap vs. E{eff. emissions} ● Indirectly the slope of the MAC vs MAB ● The discount factor

Actual EU policy Contains both crucial elements ● A quantitative target and a flat MAB, but: The ’global cap’ is not entirely fixed, e.g., CDM ● Suggests the model underestimates the optimal share to tax Trading firms may bank ’individually’ ● Suggests the model overestimates the optimal share to tax