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Environmental Policy Instruments

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If resource conservation is not required, firms are free to use natural resources. ... National ambient air quality standards (NAAQS) ... – PowerPoint PPT presentation

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Title: Environmental Policy Instruments


1
Environmental Policy Instruments
  • EEP 255
  • October 21, 2003

2
Inefficient vs. Efficient Pollution Abatement
MB
S or MAC
Private Property or Open Access Equilibrium
Efficient Equilibrium
3
Externalities
  • Costs or benefits that result from market
    activities, but are not reflected in the market
    supply or demand curves (I.e. in the decisions by
    suppliers and consumers).
  • Externalities can be positive or negative
  • Externalities can arise either from production
    (SMC?PMC) or from Consumption (SMB?PMB)

4
Private, Social, and External Costs Without
Abatement
Marginal Social Cost without abatement
Marginal Private Cost without abatement
MB
Marginal External Cost without abatement
5
Market Failure in the Private Goods Market
Marginal Social Cost (MSC)
Marginal Private Cost (MPC)
MB
Marginal External Cost (MEC)
Efficient Equilibrium
Inefficient Equilibrium
6
Terminology of Externalities
  • Marginal Social Benefits (MSB)
  • Benefits to market consumers plus benefits(or -)
    enjoyed by individuals external to the market
  • Marginal Private Benefits (MPB)
  • Benefits enjoyed by market consumers only
  • Marginal Social Costs (MSC)
  • Costs to market suppliers plus costs borne by
    individuals external to the market
  • Marginal Private Costs (MPC)
  • Marginal costs borne by market suppliers only

7
Negative and Positive Externalities
  • MSB MPB MEB (Marginal External Benefit)
  • Negative externality occurs when MEB is negative
  • Positive externality occurs when MEB is positive
  • MSC MPC MEC (Marginal External Cost)
  • Negative externality occurs when MEC is positive
  • Positive externality occurs when MEC is negative

8
Example Effect of Market Failure for Resource
Conservation on Markets for Private Goods
  • If the government does not determine the quantity
    of resource conservation, none will be produced.
  • If resource conservation is not required, firms
    are free to use natural resources.
  • This changes the firms profit functions because
    the price of raw material inputs will depend only
    on the marginal extraction cost.
  • Because production costs are lower, the supply
    curve for the firms outputs will shift to the
    right. This is shown in the next two slides.

9
Market for Resource Conservation Example of
Stock Size in a Ocean Fishery
MB
MC
Open Access Equilibrium
Efficient Equilibrium
10
Market for Harvested Ocean Fish
MSC
MSB
MPC
Efficient Equilibrium
Private Market Equilibrium
11
Marginal User Cost in the Market for Harvested
Ocean Fish
MSC
MSB
MPC
Marginal User Cost (MUC)
Efficient Equilibrium
Private Market Equilibrium
12
User Cost
  • The cost of using an asset today rather than
    saving it for a future use.
  • Its an inter-temporal externality
  • MSC-MPC MUC (marginal user cost)

13
Environmental Policy Instruments
  • EEP 255

14
Market Failure and Open Access
  • Market for environmental quality (abatement or
    resource conservation) fails to form
  • If the state does nothing about this market
    failure, there is open access to environmental
    quality
  • Open access to environmental resources results in
    an inefficient amount of environmental quality

15
Environmental Policies
  • Replace open access to the environment with state
    ownership of the environment
  • The state determines the amount of environmental
    quality (abatement or conservation) that will be
    supplied (Goal)
  • The state determines how environmental quality
    (abatement or conservation) will be supplied and
    who pays for it (Means)

16
Two Types of Environmental Policies
  • Policies that establish an environmental quality
    goal for a particular geographic area (Amount of
    environmental quality to supply)
  • Policies that establish the means by which the
    environmental policy goal will be achieved (How
    environmental quality will be supplied)

17
Example Air and Water Quality Policies
  • Ambient Standards (Goal)
  • Implementation Policies (Means)

18
Ambient Standards for Air and Water Quality
  • Air quality standards
  • National ambient air quality standards (NAAQS)
  • National emissions standards for hazardous air
    pollutants (NESHAP)-Technology based emission
    standards
  • Water quality standards
  • Use designation for all water bodies (e.g.,
    swimable, fishable, boatable, commercial)
  • Water quality criteria set to meet the designated
    use

19
An Example of an Ambient Air Quality Standard
  • Sulfur dioxide SO2 in air
  • Annual average daily concentration 80?g/ m3
  • 24-hour average concentration 365?g/ m3
  • Carbon Monoxide 8 and 1 hour average
    concentrations 10?g/ m3 and 40?g/ m3 resply.
  • Criteria pollutants Particulate matter (PM and
    PM10), SOx, CO, NOx, Ozone and Lead
  • Hazardous Air Pollutants (HAPs) eg. Coke oven
    gas, Benzene, (89 listed)

20
The Economic Question About Ambient Air Quality
Standards
What is the economically efficient
standard? Answer Where Marginal benefit(MB)
Marginal cost
of abatement (MAC)
21
The Efficient Ambient Standard
Efficient Ambient Standard
Demand for abatement (MB)
Supply of abatement (MAC)
?g/ m3 Emitted
Open Access
22
Implementation Policies for Achieving Ambient Air
Quality Standard
  • Emissions Standard
  • Abatement Technology Standard
  • Emissions Tax
  • Marketable Emissions Permit
  • Input and Output Taxes Subsidies

Direct policies
Indirect policies
23
The Economic Question About Policies for
Implementing Air Quality Standards
What is the most cost-effective implementation
policy?
24
Uniform Emissions Standard
EmissionsStandard
MAC2
MAC1
Firm 1 abates 5 and Firm 2 abates 5
Combined MAC
Total cost 35 (12.522.5)
Actual Emissions
25
Emissions Tax
MAC2
MAC1
Firm 1 abates 6 (emits 4) and Firm 2 abates 4
(emits 6)
EmissionsTax
Total abatement cost 34 (1618)
26
Tradable Emission Permit
  • Government (EPA) decides on total allowable
    emissions
  • Issues tradable emission permits
  • May sell them or allocate them on some criteria
    (grandfathering)
  • Firms are required to have permits equivalent of
    their emissions.
  • If firms have excess permits because they reduced
    emissions below the allocated permits, they can
    sell excess permits in the market to others who
    could not reduce emissions.

27
Marketable Permit
MAC2
MAC1
Firm 1 abates 6 (emits 4) and Firm 2 abates 4
(emits 6)
Permit Price
28
Effect of Abatement on Firms Output
S
S'
29
When Emissions Cannot Be Measured
  • Tax Outputs of Production
  • Higher abatement costs because the only abatement
    alternative is to supply less of the output
  • Tax Inputs to Production
  • Higher abatement costs because the only abatement
    alternative is to use less of the input

30
Negative Externality in Supply of an Output
(e.g., Electricity, Petroleum)
MSC
MPC
MSB
31
Output Tax Marginal Private Costs minus Marginal
Social Costs
MSC
MPC
MSB
TAX 2
32
Output Tax Amount of the Tax
MSC
MPC
MSB
TAX 2
33
Output Tax Buyer and Seller Prices
MSC
MPC
MSB
Buyers Price 5
Suppliers Price 3
34
Output Tax Government Revenue
MSC
MPC
MSB
Buyers Price 5
Govt Revenue 2 x 2
Suppliers Price 3
35
Effect of Input Tax on Supply of an Output
S
S
MSB
36
Resource Conservation Policies
  • Taxing resource use
  • Subsidizing resource conservation

37
Other policy instruments
  • Bargaining and legal tort mechanisms
  • Public disclosure and pressure
  • Industry Voluntary programs
  • EPA voluntary programs
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