Chapter 11 Audits, enforcement and moral hazard. Last lecture was about adverse selection Polluters could be of different types and the type was private.

Slides:



Advertisements
Similar presentations
ECON 1450 – Professor Berkowitz Lectures on Chapter 2 Tort Law Area of Common Law concerned with accidental injuries Potential defendant engages in activity.
Advertisements

Bank Competition and Financial Stability: A General Equilibrium Expositi on Gianni De Nicolò International Monetary Fund and CESifo Marcella Lucchetta.
Pablo Serra Universidad de Chile Forward Contracts, Auctions and Efficiency in Electricity Markets.
Crime Chapter 13. Purpose In this chapter we explore one of the problems associated with urban areas, crime. We introduce three tools that allow us to.
Copyright © 2008 by West Legal Studies in Business A Division of Thomson Learning Chapter 50 Environmental Law and Land Use Controls Twomey Jennings Anderson’s.
Frank Cowell: Microeconomics Exercise 11.1 MICROECONOMICS Principles and Analysis Frank Cowell March 2007.
Criteria for Evaluating Environmental Policies
Topic 3.b: Emissions taxes
Fiscal and Regulatory Enforcement Topic 10. An Example: Tax Collection The basic problem : Individuals know how much tax they owe. The Inland revenue.
Chapter Thirty-Three Law and Economics. Effects of Laws u Property right assignments affect –asset, income and wealth distributions; v e.g. nationalized.
Pollution Policy with Imperfect Information (Ch. 8)
Chapter 7 Pigouvian Fees Making Prices Work for the Environment.
Adverse Selection Asymmetric information is feature of many markets
Bertrand Model Matilde Machado. Matilde Machado - Industrial Economics3.4. Bertrand Model2 In Cournot, firms decide how much to produce and the.
Uncertainty, Monitoring & Enforcement Using economic models to help inform which instruments are most effective at controlling pollution.
PCP Microeconomics Session 12 Takako Fujiwara-Greve.
Chapter 4 Conventional Solutions to Environmental Problems Command-and-Control Approach © 2007 Thomson Learning/South-Western Callan and Thomas, Environmental.
LECTURE #9: MICROECONOMICS CHAPTER 10
Chapter 14 – Efficient and Equitable Taxation
Uncertainty, Monitoring & Enforcement Using economic models to help inform which instruments are most effective at controlling pollution.
Chapter 17 Externalities and the Environment © 2009 South-Western/ Cengage Learning.
Fashioning Incentive Contracts for Managers Such contracts may be implicit or explicit Such contracts may be implicit or explicit We’re talking here about.
Frontiers of Microeconomics
Policy objectives & targets Pollutants - (negative) externalities: “exist when some of the consequences of production (pollution’s imposing costs on others)
Regulating negative environmental externalities of agriculture Lecture 20 Economics of Food Markets Alan Matthews.
Frank Cowell: Microeconomics Exercise 11.3 MICROECONOMICS Principles and Analysis Frank Cowell March 2007.
Game Theory “A little knowledge is a dangerous thing. So is a lot.” - Albert Einstein Topic 7 Information.
Principal - Agent Games. Sometimes asymmetric information develops after a contract has been signed In this case, signaling and screening do not help,
Environmental Economics Class 7. Incentive Based Regulation: Basic Concepts Up to this point, the focus has been on resource allocation. Since the use.
Externalities. What is an externality?  the uncompensated impact of one person's actions on the well- being of a bystander (or 3 rd party) Two Types.
Our final lecture analyzes optimal contracting in situations when the principal writing the contract has less information than the agent who accepts or.
More on Stock Pollutants followed by the Environment and Asymmetric Information Lecture ECON 4910.
Comprehensive Volume, 18 th Edition Chapter 52: Environmental Law and Land Use Controls.
3.1. Strategic Behavior Matilde Machado.
Asymmetric Information
Review: Insurance Idea of risk aversion in money. –Not dislike of risk, but –Declining marginal utility of income. –Provides one reason to have insurance.
Is Deposit Insurance a Good Thing, and if so, Who should pay for it? Alan Morrison, Merton College & Saïd Business School, Oxford Lucy White, Harvard Business.
Frank Cowell: Microeconomics Contract Design MICROECONOMICS Principles and Analysis Frank Cowell Almost essential Adverse selection Almost essential Adverse.
Environmental Economics1 ECON 4910 Spring 2007 Environmental Economics Lecture 1 Lecturer: Finn R. Førsund.
Industrial Organization- Matilde Machado The Hotelling Model Hotelling Model Matilde Machado.
Environmental Economics1 ECON 4910 Spring 2007 Environmental Economics Lecture 6, Chapter 9 Lecturer: Finn R. Førsund.
Seminar Exercise 3 ECN Exercise 1 a) For the problem to make sense a > d. Social welfare is maximised by solving the following problem: max x 
Chapter 4 Conventional Solutions to Environmental Problems: Command-and-Control Approach.
Commercial and Political Efficiency Lecture Notes, Part Two January 28, 2004.
Managerial Effort Incentives and Market Collusion Cécile Aubert University of Bordeaux (GREThA) and Toulouse School of Economics (LERNA) ACLE 2009.
Chapter 4 The Adverse Selection Problem Stefan P. Schleicher University of Graz Economics of Information Incentives and Contracts.
Approaches to Curtail the Production of Environmental Bads by the Agricultural Industry 1) Performance Based 2) Design Based 3) Market Based 4) Liability.
Lecture 5 Financial Incentives This lecture is paired with our previous one that discussed employee benefits. Here we focus on the reasons why monetary.
Lecture 1 in Contracts Nonlinear Pricing This lecture studies how those who create and administer organizations design the incentives and institutional.
Summing up1 ECON 4910 Spring 2007 Environmental Economics Lecture 12 Summing up Lecturer: Finn R. Førsund.
Externalities >> chapter: 17 Krugman/Wells Economics ©2009  Worth Publishers 1 of 32.
A Supplier’s Optimal Quantity Discount Policy Under Asymmetric Information Charles J. Corbett Xavier de Groote Presented by Jing Zhou.
Frank Cowell: Contract Design CONTRACT DESIGN MICROECONOMICS Principles and Analysis Frank Cowell July Almost essential: Adverse selection Almost.
Frank Cowell: Microeconomics Moral Hazard MICROECONOMICS Principles and Analysis Frank Cowell Almost essential Risk Almost essential Risk Prerequisites.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 13 Economics of Pollution Control: An Overview.
Unknown control costs1 ECON 4910 Spring 2007 Environmental Economics Lecture 10, Chapter 10 Lecturer: Finn R. Førsund.
Unknown control cost1 ECON 4910 Spring 2007 Environmental Economics Lecture 11, Chapter 10 Kolstad Lecturer: Finn R. Førsund.
A. CAUSAL EFFECTS Eva Hromádková, Applied Econometrics JEM007, IES Lecture 2A.
The political economy of government debt Advanced Political Economics Fall 2011 Riccardo Puglisi.
Uncertainty, Monitoring & Enforcement Using economic models to help inform which instruments are most effective at controlling pollution.
Q 2.1 Nash Equilibrium Ben
APRIA 2014 Annual Conference
Externalities.
Economics of Pollution Control: An Overview
ECON 4910 Spring 2007 Environmental Economics Lecture 6, Chapter 9
MICROECONOMICS Principles and Analysis Frank Cowell
ECON 4910 Spring 2007 Environmental Economics Lecture 3, Chapter 7 -9
Economics of Pollution Control: An Overview
Chapter Thirty-Three Law and Economics.
Lecturer: Finn R. Førsund
Presentation transcript:

Chapter 11 Audits, enforcement and moral hazard

Last lecture was about adverse selection Polluters could be of different types and the type was private information The source of the regulators problem was to regulate without knowing the type. This is only one of a large number of problems with enforcing environmental regulation Today’s topic is ”Hidden actions”

The problem with democracies and civilisation The economically optimal punishment for any crime is to hang people with probability zero. The punishment should be so severe that no- one wants to commit crimes. Alas, even the harshest punishment regimes do not deter all criminals. People commit crimes by mistake. In courts severe punishment may be counter- productive as judges and juries are human and prefer to let people go rather than impose extreme punishments.

The cost of hidden actions. A regulator can impose a standard but cannot observe emission levels. (I.e. can not tax or directly regulate emissions.) The cost to the firm of technology a and emission level f is given by C(a,f). Emissions are given by e(a, f). Damages are given by D(e). The firm wants to minimise C(a,f). The regulator wants to minimise D(e) + C(a,f). (Maximise respectively -C(a,f) and –(D(e) + C(a,f))

The optimal solution First order conditions aa –D’e’ a – C’ a = 0 ff –D’e’ f – C’ f = 0 Gives the solution that the regulator would choose if she could observe f.

The game Regulator choose a. Then the firm choose f. Stackelberg game solved by backwards induction. We first find the firm’s optimal choice of f as a function of a, and then find the regulator’s optimal a

The firms problem Maximising -C(a,f) implies C’ f (a, f) = 0. Gives firm’s f as a function h(a). The derivative of h depends on technology (The derivative C’’ fa (a, f) ) f C’ f (a, f)

The choice of a The regulator wishes to maximise –D(e(a,h(a)) – C(a, h(a)) First order condition is: aa = ( ff –D’e’ a – C’ a = (D’e’ f + C’ f )h’(a) ff > 0. D’e’ f + C’ f > 0. Therefore aa > 0. Too little a and vice versa. Therefore h’(a) > 0  –D’e’ a – C’ a > 0. Too little a and vice versa. D(e(a,f)) + C(a,f)

What to do? Create incentive structures These are very problem specific. We will og through a couple of examples

Unobservable emissions Two polluters emit pollution to a single receptor Only the total level of pollution at the receptor is observable Cost of pollution reduction is C i (e i ) i = 1,2. Cost of pollution is D(p) = D(a 1 e 1 + a 2 e 2 ). Optimal level of pollution is given by: –dC i (e i )/de i = a i D’(p*). i = 1,2.

Incentive compatible scheme We can’t impose tax on emissions as we can not monitor them. Let us try taxing pollution. Tax paid by polluter i is given by: T i = t(p – p*) Polluter i then faces the cost of pollution TC(e i ) = C i (e i ) + t(p – p*) = C i (e i ) + t(a 1 e 1 + a 2 e 2 – p*)

The outcome for polluters F.o.c for polluters: dC i (e i )/de i + ta i = 0 Optimal tax is then D’(p*) because that implies that dC i (e i )/de i =– D’(p*)a i which is the optimality condition Without observing actions we still can impose optimal taxes! Problematic approach if there are more than a few polluters

Midnight dumping Making polluters dump their waste in the right place. It is cheap to dump it in the mayor’s garden. It is expensive to have it safely disposed of. Waste is only observed when it is created and if it is safely disposed If waste is dumped illegally TC(w) = C i (w). If safely disposed TC(w) = C s (w) – sw. s is a waste disposal subsidy. Problem: With this scheme tha polluter has an incentive to create w. It becomes a waste factory.

Using both taxes and subsidies If waste is dumped illegally TC(w) = C i (w). If safely disposed TC(w) = C s (w) – sw + tw. t is a waste production tax. t and s must solve two problems: –Make waste production efficient given that the polluter disposes w safely –Ensure that the polluter actually deposits all waste safely.

This gives the regulator two constraints Make waste production efficient given that the polluter disposes w safely F.o.c : dC s (w s )/dw s – s + t = 0. Ensure that the polluter actually deposits all waste safely. C s (w) – sw + tw.  C i (w unregulated )

The regulators problem min s,t (C s (w) + D s (w) +  (sw - tw)) subject to the constraints.  is here the social cost of taxation. s must be taken from somewhere. t can be returned. A problem with two constraints and two variables. In general, both constraints will be binding so there really is not much to optimize.

Enforcement Here a polluter choose a pollution level. The emissions may not be observed, but can be revealed through an audit. The firm faces penalties for increasing e above some level s*. F(e) = 0 for e  s* F(e) = πf(e – s*) + D for e > s* Total cost of emission reductions T(e) = C(e) + F(e)

Two cases First case: relatively high D, f and π

Two cases Second case: Relatively low D, f and π

Auditing with more detail Assume there is a probability p of an accident where emissions are given by . The regulator wants the firm to produce something which requires emissions, but not too much emissions. The regulator does not know whether emissions are caused by accident or by non-compliance

A model With probability (1 – p) emissions are e, damages are D(e) and costs are C(e). With probability p, emissions are , damages are D(  ) and costs are C(e). Optimal emissions are defined by: min e (p(C(e)+D(e)) + (1– p)(C(e)+D(  ))) Foc: C’(e) = pD’(e)  optimal e = s*

Incentive structure The firm minimise: H(e) = p(F(e)+ C(e)) + (1 – p)(F(  )+ C(e)) if they comply. Incentive compatability requires H(s*) > H(  ) Participation constraint requires H(s*) > H(0) (Only one of these constraints will be binding) Efficency requires s* = argmin e H(e)

Regulators problem Given that e should be s*, the regulator chooses to minimise the cost of auditing. That is πk. By choosing large D and f, π can be chosen as small as one wants, that is some ε above 0.