administrative science paper is due 5pm, friday, march 27 –questions? –office hours- after class...
TRANSCRIPT
Administrative
• Science paper is due 5pm, Friday, March 27– Questions? – Office hours- after class today; Tuesday –till 3
• ES Advising Session– 5pm tonight– Dana 285
Business School
• Businesses seek competitive advantage by reducing costs & product differentiation. M. Porter
• Social License theory– Esty and Winston
Political Economy (Chicago School)
• Corporations seek competitive advantage via public policy. G. Stigler
Baptists Bootleggers
• Companies• Industries• Countries
Command and Control
Regulatory Decision-making
• Decisions by Expert Choice
• High Knowledge Demands
• High Performance Information Demands
• Monitoring & compliance• Enforcement• Bureaucracy Growth
Economists’ Critique
• C & C Regulation is Inefficient
• “One size fits all” rules• Does not recognize that it is
easier and cheaper for• some polluters to reduce
pollution than others• Few incentives for innovation• Few incentives for voluntary
compliance• High transaction costs
Discourses
• “A discourse is a shared way of apprehending the world. Embedded in language, it enables those who subscribe to it to interpret bits of information and put them together into coherent stories or accounts. Each discourse rests on assumptions, judgments, and contentions that provide the basic terms for analysis, debates, agreements, and disagreements”– John Dryzek, The Politics of the Earth, 1997
Economist Discourse
Environmental Degradation
• Causes • Optimal Levels• Pollution as subsidy
Economists Perspective?
Foxconn Factory in Shenzhen
500 million iPhone uses later....
Implications
• Should only do pollution control if benefits are worth more than values we forgo.
• Means of achieve pollution control targets should minimize costs of meeting targets
Marginal Costs
Air Quality in New DelhiU.S. Embassy Air Quality Monitor
NYC Monitoring of short- and long-term PM2.5 concentrations in ambient (outdoor)
•5 percent above the annual standard in 2003 to 22 percent below in 2013.
•14 percent above the 24-hour standard in 2003 to 26 percent below in 2013
•How - ultra-low diesel fuel, LEV, factory regulations
BUT (2,300 premature deaths, 4,800 emergency room visits for asthma, and 1,500 hospitalizations for respiratory and cardiovascular disease.
Achieves Attainment with U.S. Environmental Protection Agency National Ambient Air Quality Standards for Particulate Matter, http://www.dec.ny.gov/press/96759.html
Should NYC Decrease Pollution
Marginal Costs and Efficiency
• To maximize societal benefits, we should allocate it to where marginal costs of clean are the least.– Ducks vs. Chickens
• If you can spend $100 to remove SO2– Firm A $5 ton– Firm B $10 – Firm C $20
Market Policy Instruments
• provide incentives for businesses and individuals to act in ways that further their own financial goals, but also the environment.
• leave the choice of how to accomplish this up to individuals or companies concerned.
• use economic instruments such as prices, taxes, subsidies, bonds, liability, or markets to align individual incentives with the common good
Examples?
Market Mechanisms
Cons, say political scientists
• Equity• Disproportionate impact• Fairness• Losers more visible
Pros, say economists
• Innovation• Neutral• Efficient
Selling Indulgences
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
In the next slide we will evaluate a numerical example of a hypothetical industry that is required to reduce its overall emissions by 50 percent. We will first derive compliance costs for this level of pollution control under a performance-based standard, and then we will derive compliance costs for the same level of pollution control under a cap-and-trade system.
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
Case 1: Cut overall industrial emissions by 50 percent using a performance-based standardperformance-based standard, (command and control) which requires that each firm cut its emissions by 50 percent.
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
Firms Historical Emissions(Tons/Yr)
Marginal Abatement Cost ($/Ton)
Tons of Emissions to be Reduced
Total Abatement Cost (No Tradable Allowances)
Alkyone 600 50 300
Merope 600 100 300
Kelaino 600 100 300
Elektra 600 150 300
Sterope 800 200 400
Taygete 800 250 400
Maia 800 400 400
Industry Total
4,800 --- 2,400
Fill in this column
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
You should have found that the industry wide cost of compliance under the performance-based
standard was $460,000.
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
Case 2: Cut overall industrial emissions by 50 percent using a cap-and-trade systemcap-and-trade system. Assume that quota shares are fully tradable and (perhaps unrealistically) that firms can fully eliminate emissions and still produce.
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
Firms Historical Emissions(Tons/Yr)
Marginal Abatement Cost ($/Ton)
Allowances (Allowed Emissions)
Alkyone 600 50 300
Merope 600 100 300
Kelaino 600 100 300
Elektra 600 150 300
Sterope 800 200 400
Taygete 800 250 400
Maia 800 400 400
Industry Total 4,800 --- 2,400
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
To answer the question of what total industry-wide compliance costs will be in a cap-and-trade system, we must first determine the pattern of trade.
Which firms buybuy allowances and which firms sellsell allowances, and why?
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
If a firm has highhigh pollution abatement costs, can it reduce them by purchasing allowances from a firm with low pollution abatement costs?
Note that when a firm buys an allowance, it is allowed to emit an additional 1 ton of pollution for a year, and thus saves on the cost of reducing its emissions by 1 ton.
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
Firms Historical Emissions(Tons/Yr)
Marginal Abatement Cost ($/Ton)
Alkyone 600 50
Merope 600 100
Kelaino 600 100
Elektra 600 150
Sterope 800 200
Taygete 800 250
Maia 800 400
Industry Total
4,800 ---
In this example, could Alkyone make a profit by selling an allowance to Maia for $200? How much?
Is this purchase advantageous for Maia? By how much?
Numerical Example of the Cost Savings Associated with Cap-and-Trade Systems
Note: To solve for case 2 (fully tradable allowances), be sure that total allowances bought equals total allowances sold, and that all available gains from trade are realized. You should find that the total cost of compliance with a 50 percent industry-wide emissions reduction is
$240,000$240,000.
Reducing industry wide emissions under the performance-based standard was $460,000. Thus the cost savings here are
$220,000.
Cap and Trade Program Basics
• Set an emissions tonnage limit (cap or budget) for a class of sources in a region.
• Allocate the right to emit tons (allowances or permits) to individual sources.
• At the end of the season, each source must have allowances equal to actual emissions.
• Sources can control, overcontrol, sell, bank, buy allowances to comply.
Elements of a Successful Cap-and-Trade System
• Determine an overall maximum level of emissions (the "cap"). • Assign polluters an individual pollution quota or allowance,
usually based on emissions levels in some baseline year; the sum of these allowances is equal to the desired level of emissions.
• Let these allowances be tradable to some degree.• Require new firms to buy allowances from existing firms.• Create a market institution that minimizes the transaction cost of
trades.• Monitor and enforce sanctions against those that pollute above
and beyond their allowance, so firms have an incentive to buy allowances rather than freely pollute.
• Maintain policy stability over time so, for example, firms are willing to buy permits knowing that standards will not be lifted in the future.
NOX
80006000400020000-2000
MW3000
2000
1000
0
-1000
6000050000400003000020000100000-10000
3000
2000
1000
0
-1000
MW
NOX
MW
SOX
NOX
80006000400020000-2000
CO
AL
1.2
1.0
.8
.6
.4
.2
0.0
-.2
NOX
80006000400020000-2000
SC
RU
B
1.2
1.0
.8
.6
.4
.2
0.0
-.2
NOX
80006000400020000-2000
MW
3000
2000
1000
0
-1000
COAL
1.00
.99
.98
.96
.86
.48
.00
SOX
6000050000400003000020000100000-10000
MW
3000
2000
1000
0
-1000
COAL
1.00
.99
.98
.96
.86
.48
.00
Acid Deposition Process
Source: EPA
Acid Deposition Process
Sulfur dioxide (SO2) and nitrogen oxides (NOx) are the primary causes of acid rain. In the US, About 2/3 of all SO2 and 1/4 of all NOx comes from electric power generation that relies on burning fossil fuels like coal.
Acid rain occurs when these gases react in the atmosphere with water, oxygen, and other chemicals to form various acidic compounds. Sunlight increases the rate of most of these reactions. The result is a solution of sulfuric acid and nitric acid.
Has Acid Rain Cap and Trade Worked?
• Environmental
• Economic
• Political
SO2 Environmental Results: The Cap and Trade Platform
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
1.60
1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000
Ind
ex
: 1
98
7 =
1.0
U.S. Gross Domestic Product
Total net electricity generation
SO2 emissions from electric utilities
(Sources: DOC, DOE and EPA, respectively)
*
* ARP units only
Historical Approach to Cap and Trade
• Fixed levels
• Large, step reductions
• Allocation based on historic heat input
• Participation limited to fossil generators
• New and clean units treated less favorably
Critical Design Elements
• Setting cap levels and timing
• Applicability
• Allocation of Allowances
Historical Problems With Caps• Difficult to find the right cap level.• Allocation favors historic big polluters.• Doesn’t include/support new, efficient
generators.• Under a cap, command and control programs
provide no environmental value since total emissions will remain the same.– Command and control defeats the trading
program benefit of reducing costs.
Traditional Emission Cap Profile
0
1
2
3
4
5
6
7
8
9
10
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016
Year
MM
Ton
s
Non-Title IV Sources
Example of Declining Cap on SO2
0
1
2
3
4
5
6
7
8
9
10
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019 2020
MM
Ton
s
Declining Cap10%/yr
Jeffords
BAU
Non-Title IV Sources
Bush
Declining Cap/Circuit breaker
• Each cap decreases by fixed percent each year. Glide slope defined in advance.
• Decline for each pollutant stops if annual average allowance cost exceeds predetermined cost threshold ($/ton).
• Decline starts again when the annual average cost is below threshold.
Illustration of Declining Cap
0
20
40
60
80
100
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15
Year of Program
0
100
200
300
400
500
600
Cap Level(Tons/year) Circuit Breaker Value
($/ton)
Allowance Price
Allocation Options
• Grandfathering primarily rewards old, high emitting plants.- Think Maia
• Auction has theoretical benefits but is politically difficult.
• Output-based, reallocating program provides maximum reward for efficiency, low emissions, new plants.
Principles for CO2 Regulation
• Climate change is a long-term problem. We need to look for long-term solutions.
• Short-term massive switching to gas detracts from development of longer term solutions and may not be sustainable.
• More gradual path to the longer-term solutions will be more productive.
– Renewables– Efficiency
– Clean coal– Sequestration
The CO2 Approach Must:
• Limit economic risk• Limit large structural
or lifestyle changes• Not pick winners• Be market-based
• Show a commitment• Be gradual• Promote new
technology• Lead to commitments
from other countries
Proposed Approach
• Replace inefficient command and control regulation with an appropriate cap and trade program.
• Design cap and trade program to:– Better encourage diverse mix of clean
technologies and efficiency.– Promote technology development.– Ensure better environmental performance.
No More Free Dumping
“Since the dawn of the industrial revolution,
the atmosphere has served as a free
dumping ground for carbon gases. If people
and industries are made to pay heavily for
the privilege, they will inevitably be driven to
develop cleaner fuels, cars and factories.”
— Avoiding Calamity on the Cheap, Nov. 3, 2006New York Times editorial
Allocation OptionsFirms Historical
Emissions(Tons/Yr)
Marginal Abatement Cost ($/Ton)
Tons of Emissions to be Reduced
Total Abatement Cost (No Tradable Allowances)
Alkyone 600 50 300
Merope 600 100 300
Kelaino 600 100 300
Elektra 600 150 300
Sterope 800 200 400
Taygete 800 250 400
Maia 800 400 400
Industry Total
4,800 --- 2,400
Fill in this column
Allocation Effects on Companies
Do Better Under Output* Do Worse Under Output
Southern Co. AEP TVA Reliant Cinergy Progress Energy Duke Energy Allegheny Energy DTE Energy Domminion FirstEnergy FPL PPL
Xcel TXU Entergy Edison International Scottish Power Ameren LG&E MidAmerican Energy Pinnacle West
*Within 1%
What are the challenges to reducing carbon emissions?
Principles for CO2 Regulation
• Climate change is a long-term problem. We need to look for long-term solutions.
• Short-term massive switching to gas detracts from development of longer term solutions and may not be sustainable.
• More gradual path to the longer-term solutions will be more productive.
– Renewables– Efficiency
– Clean coal– Sequestration
The CO2 Approach Must:
• Limit economic risk• Limit large structural
or lifestyle changes• Not pick winners• Be market-based
• Show a commitment• Be gradual• Promote new
technology• Lead to commitments
from other countries
Proposed Approach
• Replace inefficient command and control regulation with an appropriate cap and trade program.
• Design cap and trade program to:– Better encourage diverse mix of clean
technologies and efficiency.– Promote technology development.– Ensure better environmental performance.
What are advantage of cap and trade for global warming?
Cap and Trade Programs
• Cap provides greater environmental certainty than command and control.
• Provides greater flexibility and lower compliance cost.
• With proper design, can encourage efficiency and new technology.
Congressional Cap and Trade
• Bingaman-Specter (S 1766)• Udall-Petri (Draft, May 2007)• Lieberman-McCain (S 280)• Kerry-Snowe (S 485)• Waxman (HR 1590)• Sanders-Boxer (S 309)• Feinstein-Carper (S 317)• Alexander-Lieberman (S 1168)• Stark (HR 2069)• Larson (HR 3416)
John Dingell Cap-and-Trade Program
• $50-per-ton tax on carbon
• 50 cents per gallon tax on gasoline and jet fuel
• Indexed to inflation• “No New Taxes”
Regressivity/Rebates
John Dingell (D-MI-Auto)
John Dingell Hybrid Carbon and Petroleum Tax Bill
• $50-per-ton tax on carbon
• 50 cents per gallon tax on gasoline and jet fuel
• Indexed to inflation• “No New Taxes”
Regressivity/Rebates
John Dingell (D-MI-Auto)
Arguments for a Carbon Tax
Effectiveness and Efficiency
Wide Array of Support
• .
Control on Price Not Quantity
• “Specifically, a carbon tax equal to the damage per ton of CO2 will lead to exactly the right balance between the cost of reducing emissions and the resulting benefits of less global warming.” William Pizer
• “Corrective taxes are superior to direct regulation of harmful externalities when the state's information about control costs is incomplete."
AEI, Climate Change: Caps vs. Taxes, 2007
What is the Behavioral Impact on Firms and Consumers?
Why the Changs?
Impact of Carbon Tax on Emissions and Revenue
Equity Implications
• Who gets hit hardest by Carbon Tax?
Reduction in Taxes
Double Dividend
• Mitigate economic costs of tax– Lower capital/corporate taxes– Lower payroll taxes, offset regressive effects– Invest in energy efficiency
Predictability
• No fluctuation in prices
Caveats
• India and China
• US can only impose a national system
• "no regrets" principle
Political Support for Cap and Trade