Trading and Efficiency © 1998, 2006 Peter Berck. Topics Marginal Cost of abatement and Bid for Permits Efficient Allocation of Emissions among firms Cap.

Slides:



Advertisements
Similar presentations
PART 10 Market Failures Markets may fail to generate efficient results due to Monopoly Externalities Public Goods Open Access Markets may also have informational.
Advertisements

A P.O. Is a C.E. © 1998, 2007 by Peter Berck. What Is It Good? Sum of surplus and profits allows for policies that make income less evenly distributed.
1 Chapter 14 Practice Quiz Environmental Economics.
The Efficiency Standard. Introduction  Proponents of efficiency argue: balance the costs and benefits of pollution reduction and seek to achieve the.
In chapter 10, we look for the answers to these questions:
Lectures in Microeconomics-Charles W. Upton Barriers to Economic Efficiency.
1 Chapter 3 Externalities and Public Policy. 2 Externalities Externalities are costs or benefits of market transactions not reflected in prices. Negative.
Externalities.
SUNK COSTS & THE EXTERNALITIES 1. Index 1. Sunk costs Sunk costs 2. Shubik’s Theory Shubik’s Theory 3. Ernest Dupuis III Ernest Dupuis III 4. Sunk costs.
7.2 Externalities Externalities and Missing Markets 7.2.2Coase Theorem 7.2.3Intervention 7.2.4Summary.
Intermediate Microeconomic Theory
1 Topic 2: Production Externalities Examples of types of abatement activities analyzed: –Output reduction –Cleaner production involving  VC (ex: input-switching)
1 Topic 3.c: Transferable emission permits We will start analyzing the last policy we will look at for pollution control. –Tradable/transferable emission.
1 Externality Here we study the situation where production leads to not only private costs, but also social costs.
EXTERNALITIES Chapter 5.
19 Externalities The market tends to overproduce. Spillover CostsSpillover Benefits The market tends to underproduce.
© 2008 Prentice Hall Business Publishing Economics R. Glenn Hubbard, Anthony Patrick O’Brien, 2e. Fernando & Yvonn Quijano Prepared by: Chapter 5 Externalities,
Chapter 17 Externalities and the Environment © 2009 South-Western/ Cengage Learning.
Externalities Today: Markets without ownership usually lead to inefficient outcomes.
Chapter 21 The Environment Copyright © 2010 by The McGraw-Hill Companies, Inc. All rights reserved.McGraw-Hill/Irwin.
1 External Costs. 2 Overview An externality is a situation where a third party is affected by an economic activity. The externality can be either positive.
Barriers to Economic Efficiency. The Basic Theorem in Welfare Economics A market, exchange, economy will achieve efficient resource allocation.
The Welfare Theorem & The Environment © 1998, 2011 by Peter Berck.
When you have completed your study of this chapter, you will be able to C H A P T E R C H E C K L I S T Explain why negative externalities lead to inefficient.
Harcourt, Inc. items and derived items copyright © 2001 by Harcourt, Inc. Environmental Economics.
Externalities ECO 230 J.F. O’Connor. Topics Nature of externalities Why do externalities cause market failure Private solutions to an externality problem.
General Equilibrium and the Efficiency of Perfect Competition
Externalities and Environmental Policy Chapter 5.
Chapter 2 Externalities and the Environment McGraw-Hill/Irwin
Permits and the U.S. Acid Rain Program (ARP). Acid Rain Caused primarily by SO2 and Nox, which is generated largely by coal fired plants Harmful to trees,
Review for Exam 1 Chapters 1 Through 5. Production Possibilities Frontiers and Opportunity Costs Learning Objective 2.1 Production possibilities frontier.
Copyright © 2002 by Thomson Learning, Inc. Chapter 3 Externalities and Public Policy Copyright © 2002 Thomson Learning, Inc. Thomson Learning™ is a trademark.
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.
Introduction Externalities arise whenever the actions of one party make another party worse or better off, yet the first party neither bears the costs.
Environmental Economics Of Cows and Cars Peter Berck.
Profits, Shutdown, Long Run and FC © 1998,2010 by Peter Berck.
PPA 723: Managerial Economics Lecture 19: Externalities and Public Policy The Maxwell School, Syracuse University Professor John Yinger.
Chapter 14 Economic Efficiency and the Competitive Ideal ECONOMICS: Principles and Applications, 4e HALL & LIEBERMAN, © 2008 Thomson South-Western.
Copyright © 2008 Pearson Addison-Wesley. All rights reserved. Chapter 17 The Economics of Environmental Protection.
Externalities and Public Policy
PPA 723: Managerial Economics Lecture 18: Externalities The Maxwell School, Syracuse University Professor John Yinger.
Sometimes externality problems can’t be solved by private bargaining (transaction costs are too big). Public policy toward externalities. “Command-and-control”
Across the country, countless people have protested, even risking arrest, against the Keystone XL Pipeline. (Credit: modification of image by “NoKXL”/Flickr.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 13 Economics of Pollution Control: An Overview.
MICROECONOMICS Chapter 5 Efficiency and Equity
Market Failure Chapter 14 Externalities. Economic Freedom Economic freedom refers to the degree to which private individuals are able to carry out voluntary.
12 | Environmental Protection and Negative Externalities The Economics of Pollution Command-and-Control Regulation Market-Oriented Environmental Tools.
Chapter 10 Externalities. Market Failure Market failure is when the free market does not provide the best outcome for society. Monopoly is a form of market.
A P.O. Is a C.E. © 1998 by Peter Berck. What Is It Good? §Sum of surplus and profits allows for policies that make income less evenly distributed. §A.
Trading and Efficiency © 1998, 2006 Peter Berck. Topics Marginal Cost of abatement and Bid for Permits Efficient Allocation of Emissions among firms Cap.
Externalities ECO 230 J.F. O’Connor. Topics Nature of externalities Why do externalities cause market failure Private solutions to an externality problem.
MICROECONOMICS: Theory & Applications By Edgar K. Browning & Mark A. Zupan John Wiley & Sons, Inc. 11 th Edition, Copyright 2012 PowerPoint prepared by.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 13 Economics of Pollution Control: An Overview.
ExternalitiesExternalities. Overview Externalities –Negative: Action by one party imposes a cost on another party –Positive: Action by one party benefits.
The Welfare Theorem & The Environment © 1998 by Peter Berck.
Topic 4 : Externalities. Definition of Externality An externality is an economic cost or benefit that is the by-product of economic activity but that.
Topics Externalities. The Inefficiency of Competition with Externalities. Regulating Externalities. Market Structure and Externalities. Allocating Property.
Chapter 3 – Market Failure
The Welfare Theorem & The Environment
Externalities.
Economics of Pollution Control: An Overview
C h a p t e r 3 EXTERNALITIES AND GOVERNMENT POLICY
Trading and Efficiency
Chapter 2 Externalities and the Environment McGraw-Hill/Irwin
Trading and Efficiency
Economics of Pollution Control: An Overview
Economics of Pollution Control: An Overview
The Welfare Theorem & The Environment
Taxes, Standards and Tradable Permits
Trading and Efficiency
Presentation transcript:

Trading and Efficiency © 1998, 2006 Peter Berck

Topics Marginal Cost of abatement and Bid for Permits Efficient Allocation of Emissions among firms Cap and Trade Program Coase Theorem

Reminder… A Pareto improving exchange is one that makes at least one party better off and no party worse off. Market transactions (without externalities) between willing buyers and sellers are pareto improving. A redistributive tax is not. (Makes Larry Ellison worse off and John on the corner better off.)

MCA Let E be current emissions E0 be initial emissions E0-E is abatement C(Q,E) Costs go down when emissions go up. Reducing emissions from E to E-1 is abating emissions by one unit. MCA = C(Q,E-1) – C(Q,E) Called Marginal Cost of Abatement

Abating 4 Units of Clean Air Technique (20,50) costs 180 and is least cost way to make Q* using 20 units of air P other stuff = 2.

MCA MCA = ( )/4

How much to pay for added E Firm has rights to emit E and is offered rights to emit E+1. Would pay added profits for added E This is the bid for E In a market those with highest bid get the E

Firm’s Bid for Clean Air Services Profits as a function of effluent standard (E)  (P,E) = P Q(.) - C(Q(.),E) where Q(P,E) is the supply function Firms will bid the amount of additional profits they could make from one additional unit of air (E+1) to receive one additional unit of air. Bid(E) =  (P,E+1)-  (P,E)

Q is a function of E P = MC(Q,E) Supply function is Q(P,E) – Increase in P – Increase in E P MC(Q,E+1) MC(Q,E) Q(E+1)Q(E)

Bid in terms of Cost Bid(E) =  (P,E+1)-  (P,E) = P(Q(P,E+1) –Q(P,E)) + C(Q(P,E), E) - C(Q(P,E+1), E+1) true if “1” is small relative to Q Approximately the same as Bid(E) = = P(Q(P,E+1) –Q(P,E)) + C(Q(P,E), E) - C(Q(P,E), E+1) +C(Q(P,E), E) – C(Q(P,E+1), E)

Simplifying C(Q(P,E), E) - C(Q(P,E), E+1) Is Marginal cost of abatement Negative of the change in cost from adding a unit of emission +C(Q(P,E), E) – C(Q(P,E+1), E) MC is (change in cost from one more unit of Q) MC * (Q(P,E)- Q(P,E+1)) is change in cost from (Q(P,E)- Q(P,E+1)) of Q. Notice it is a negative number

Putting it together Bid(E) = P(Q(P,E+1) –Q(P,E)) + C(Q(P,E), E) - C(Q(P,E), E+1) +C(Q(P,E), E) – C(Q(P,E+1), E) Bid(E) = (P – MC )(Q(P,E+1) –Q(P,E)) + MCA = MCA Firm’s will pay their marginal cost of abatement in order to get another unit of emissions

Bid as a function of emissions Bid = change in total cost/change in pollute Bid tons of E emitted (units of air used up)

MCA as a function of Abatement Costs more to clean up a ton as more tons cleaned up. MCA tons of abated

Trading lowers total cost

Fixed Amount of Air: Two Firms Read firm 1 from left Read firm 2 from right Point splits total between the firms. $/unit tons of E emitted (units of air used up) Total Tons To be Emitted Firm 1 emissionsFirm 2 emissions

How much Air to each? Bid is marginal cost emissions Area under bid is avoided costs Tons emitted 10 $ $7000

Bids for two firms. Bid 1 Tons emitted Bid 2 50/50 split

How much Air to each? Intersection minimizes total cost Treating firms the same has losses Bid 1 Tons emitted Bid 2 50/50 split

Dead Weight Loss Bid 1 tons Bid 2 50/50 split

Losses Older studies show that the total cost of achieving clean air is much higher with a uniform TBES than it would be with TBES set for each firm. California appears as the exception Spent much more on regulation than other states Meredith Fowlie does this with Cars and Powerplants and finds big losses from making powerplants too clean and cars not clean enough

Cap and Trade One way to get the firms to the intersection point is to give each of them a pollution allotment and let them trade. So long as they don’t trade allotments that they don’t have (fraud) the total amount of pollution remains constant Acid rains section of CAA is a Cap and Trade Program as is RECLAIM

Avoiding loss Trading. let plants within a firm let firms within an airshed Jointly meet standards Firm with higher MCA at the standard buys right to pollute from firm with lower MCA Both have more money Pollution is same.

However When two firms trade the spatial distribution of the pollution will be different. Trading can be a mechanism to inflict pollution on the poor. Trading can lead to pollution in places that are more sensitive--have more people and more health damage

Right Amount of Pollution MCA and Marginal benefit of Abatement the same. Or: Bid (firms marginal benefit from pollution) = Marginal damage from pollution Same thing.

Optimal Pollution Figure Marginal Cost and Marginal Benefit of SO x Emissions Abatement

Coase

Zero Pollution The shaded area is the deadweight loss if all 9.1 million tons of S0 x are abated.

Zero Abatement Figure Deadweight Loss if Emissions are 9.1 Million Tons

Coase Coase’s contribution was to recognize that trading is costly, sometimes prohibitively so. We call the following the Coase theorem: When trading costs are low enough, it does not matter which firms originally get the rights to pollute. The costs and pollution will be the same. But not the amounts of money the firms get (the ones with the permits get more money.)

Coase But Coase’s real contribution was to say that without trading one could get either of the DWL figures. Giving the rights to the polluter causes a lower DWL in the figures than giving the rights to the breathers. Of course, rights allocations in between do better than either.