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Valuing the Environment: Methods

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Title: Valuing the Environment: Methods


1
Chapter 3. Valuing the Environment Methods
2
Review
What is correct regarding the First Law of
Thermodynamics? a. If you use more water to
wash your hands then you should use less water
for bath. b. Your coffee should be hotter than
tea because the coffee use the water boiling for
5 minutes while the tea uses water boiling for 2
minutes.c. Energy and matter cannot be created
or destroyedd. It is about entropy.
Edited from Dr.Trudy Cameron
3
Review
What are the implications of entropy for the
long-term use of energy on Planet Earth? a.
Because of entropy, we can look forward to always
being able to use as much energy as we need. b.
In the absence of new energy, a closed system
will use up all of its energy, thus Planet Earth
is doomed to extinction when we run out of
energy c. Fortunately, the sun supplies a steady
stream of energy into the Planet Earth, so in the
long run, when we have used up our stored energy
forms such as oil, we will have to make do with
using no more energy than the sun provides for
us d. Fossil fuels are the only kind of stored
energy we have, and when we dissipate this energy
by using it for work, it will all be over.
4
Review
  • Overall total net benefits associated with
    consumption of some amount of the services of an
    environmental resource are analogous to what
    familiar concept from general microeconomics?
  • a. consumer surplus
  • b. profits
  • c. producer surplus or economic rent
  • d. the sum of producer and consumer surplus

5
Review
  • An allocation of resources over some future time
    horizon is said to be dynamically efficient if
  • a. it maximizes the present discounted value of
    net benefits across all alternative uses of these
    resources over time
  • b. if it is not statically efficient
  • c. if it maximizes the sum of the current values
    of net benefits in all future periods
  • d. if it minimizes the marginal user costs over
    time

6
Review
  • We do not have to do the benefit-cost analysis to
    any proposal if the U.S. Senate already voted.
  • True
  • False

7
Introduction
Oil Spill
8
Introduction
  • How to estimate the liabilities of damages, for
    example, Exxon Valdex oil tanker leaking?
  • Can normal valuation techniques be applied to
    environmental resources?
  • What is the current price of clean air?

9
Valuing Benefits
  • Damage estimates are used in the design of
    policies and jury judgments which is supported by
    Comprehensive Environmental Response,
    Compensation, and Liability Act.
  • It is complex and difficult to estimate the
    damages, for example, pollution control.

10
Valuing Benefits (cont.)
  • Pollution generate harms to human health that are
    recognizable in overall populations, but which
    have uncertain effects on any single individual.
    A natural example is the emission of toxic
    pollution into air or water, which elevates the
    risk of a person contracting cancer, emphysema,
    or various reproductive disorders. In this case
    one way to view the harm is the elevated
    likelihood of a person becoming ill or dying.

11
Valuing Benefits (cont.)
  • Identifying physical damages is difficult, let
    alone assigning them monetary values.
  • Neither controlled experiments nor statistical
    studies provide us satisfactory results.
  • How can we overcome these difficulties?

12
Types of Values
Stock Flow
  • A Stock
  • A Flow
  • the value of stock the present value (PV) of
    the stream of services flowing from the stock
  • If we maximize the PV of the stream of the
    services, then we use the resource efficiently.

13
Types of Values
14
Types of Values
  • Total Willingness to pay
  • Use value Option value Nonuse value

15
Example Valuing the Northern Spotted Owl
16
  • In 1990, an interagency committee proposed a plan
    to set up a habitat conservation areas from
    withdrawing certain forest areas.
  • Contingent valuation survey is conducted.
    Benefits/costs3/1
  • Survey was conducted nationally, while cost was
    shared by a small group of peoplesharing tax
    dollars

17
Classifying Valuation Methods
18
Valuation Methods
  • Contingent Valuation
  • Direct approachit asks people what they are
    willing to pay and/or what they are willing to
    accept for a change in the level of environmental
    service, in a constructed hypothetical market.
  • WTP? Hypothetical market?

19
Contingent Valuation Method
  • Hand out the experiment.

20
Contingent Valuation Method
  • How to apply CVM?
  • Set up a hypothetical market (describing the
    good, payment vehicle, rule)
  • Define the elicitation method (take-it-leave-it
    open ended)
  • Survey (on site mail telephone Internet)
  • Calculate measures of welfare changes (mean WTP)
  • Technical specification WTPif(Y, S,P, X)
  • Aggregation

21
  • CVM shortcomings
  • Strategic bias
  • Information bias
  • Starting point bias
  • Hypothetical bias
  • NOAA panel supported cautiously.
  • Meta-analysis can solve the dilemma.

22
Travel Cost Model
  • Suppose somebody introduced an exotic species
    into the Charleston Lake, such as pike.
    Charleston residents are now worrying about
    quantifying the demand for fishing days at
    Charleston Lake which has been compromised by
    predatory pike.

WTP price
Lost Consumer Surplus Benefit of clearing pike
23
Travel Cost Model
  • TCM is often used to assess the value of parks,
    lakes, and similar public areas which host a good
    deal of recreational activity, and which are far
    enough away from many people to require users to
    drive or fly to the site.
  • The basic premise of the TCM is that, although
    the actual value of the recreational experience
    does not have a price tag, the costs incurred by
    individuals in traveling to the site can be used
    as surrogate prices.

24
Travel Cost Model
  • Zonal travel cost is used to collect information
    on the number of visits to the site from
    different distances. These different distances
    can be calculated using zip codes and AAA mileage
    information.
  • The surrogate pricetravel cost time cost.
  • Researcher can construct function of number of
    visits at different prices.

25
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26
Travel Cost Model
  • Individual travel cost model uses survey data
    from individual visitors asking them about their
    number of trips to the site.
  • Researchers can use individual information such
    as income, race, age in the models.
  • This approach will provide more precise results,
    but it requires more data collection and more
    complicated statistical skills.

27
Valuing Implied Human Life
  • Estimate the implied value of death for
    reducing probabilities a certain amount. For
    example if one million people are willing to pay
    5 on average to reduce chance of death from 1 in
    100,000 to 1 in 150,000, then people are willing
    to pay 5 million dollars to reduces deaths from
    10 to 6.67 per year. 5,000,000/3.33 gives the
    value per life of 1.5 million.
  • A 1996 survey found that most implied values of
    human life were between 3 million and 7
    million.

28
Issues in Benefit Estimation
  • Primary versus Secondary Effects
  • What should be counted might vary depending on
    the nature of the local economy. Thus it will
    vary by place and time. Secondary employment
    should be considered in high unemployment areas,
    while it should be ignored if it is only a
    rearrangement. (example cleaning a lake)
  • Tangible versus Intangible Effects
  • Intangible benefits should be quantified to the
    fullest extent.
  • Sensitivity analysis is often used to measure the
    importance of the benefit.

29
Approaches to Cost Estimation
  • Estimating cost is typically more straightforward
    than estimating some types of benefits.
    Difficulties involve estimating expected future
    costs and getting reliable cost information from
    firms. Some common approaches include the
    following
  • 1.      The survey approach involves asking
    polluters about their control costs (drawback?).
  • 2.      The engineering approach uses engineering
    information to estimate the technologies
    available and the costs of purchasing and using
    those technologies (problem?).
  • 3. The combined approach uses both 1 and 2.

30
The Treatment of Risk
  • Since it is typically not practical to do a
    benefit-cost analysis for every possible outcome,
    we usually must utilize expected values.
  • 1.      A dominant policy is one which confers
    the higher net benefits in every outcome.
  • 2.      The expected value of net benefits is the
    sum over the possible outcomes of the present
    value of net benefits of that outcome weighted by
    its probability of occurrence. The policy
    selected should be the one with the highest
    expected present value of net benefits.
  • The above approach assumes risk neutrality.
    Whether or not it makes sense for the government
    to assume that society on the whole is risk
    neutral (versus risk loving or risk averse)
    should be discussed.

31
Choosing the Discount Rate
  • The discount rate is defined as the social
    opportunity cost of capital. The discount rate
    will have two components
  • the riskless cost of capital
  • and the risk premium.
  • The rate on long-term government bonds is a
    common choice as a measure of the cost of
    capital. This can then be adjusted by a risk
    premium to reflect the level of riskiness of the
    particular project being considered.

32
Cost-Effective Analysis
  • Cost-effectiveness analysis is a useful
    alternative to benefit-cost analysis when the
    measurement of benefits is impossible or
    estimates are unavailable.
  • This alternative involves the minimization of the
    costs of achieving a policy target such as an
    emissions standard. A minimum-cost solution
    requires the equalization of the marginal costs
    of all possible alternatives

33
Impact Analysis
  • Environmental impact statements attempt to
    quantify consequences of an action. Impact
    analysis is useful when the data needed for
    either a benefit-cost analysis or a
    cost-effectiveness analysis is unavailable.
  • These present the analyst with as much raw
    information as is available without any
    optimization or benefit-cost analysis. More
    sophisticated environmental impact statements
    sometimes include benefit-cost analysis or a
    cost-effectiveness analysis.

34
Problem
  • In a research paper, Mark Cohen attempted to
    quantify the marginal benefits and marginal costs
    of U.S. Coast Guard enforcement activity in the
    area of oil spill prevention. His analysis
    suggests that the marginal per-gallon benefit
    from the current level of enforcement activity is
    7.50 while the marginal per-gallon cost is
    5.50. Assuming these numbers are correct, would
    you recommend that the Coast Guard increase,
    decrease, or hold at the current level their
    enforcement activity? Why?
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