Valuation 5: The Contingent Valuation Method • Direct and indirect valuation methods • Total economic value revised • History of CVM • Welfare measures with the CVM • CVM study design • Validity, reliability, biases • Example: Seoul water
Dec 18, 2015
Valuation 5: The Contingent Valuation
Method• Direct and indirect valuation methods • Total economic value revised• History of CVM• Welfare measures with the CVM• CVM study design• Validity, reliability, biases• Example: Seoul water
Last week
• Why econometrics? • What are the tasks?• Specification and estimation• Hypotheses testing• Example study
Direct & Indirect Valuation
• Direct methods – Constructed markets
• Contingent valuation method (CVM)• Choice modelling
Stated preference methods• Indirect methods
– Surrogate market• Hedonic pricing• Travel cost
Revealed preference methods
Geographic Characteristics
71
280
823
1131
41
0
200
400
600
800
1000
1200
Af rica Asia Europe North
America
South
AmericaSource: www.evri.ec.gc.ca
Valuation Technique
324
560
1427
0
200
400
600
800
1000
1200
1400
1600
Actual Revealed Stated
Environmental Assets
221
616
332
576
321
725
0
100
200
300
400
500
600
700
800
Air Animals Human Land Plants Water
Source: www.evri.ec.gc.ca
Environmental Goods and Services Valued
159
423
808
380
891
460
0
200
400
600
800
1000
Bui lt
environment
Ecological
f unctions
Extractive
use
Human health Non-
extractive
use
Passive use
Total Economic Value of Nature Goods & Services
Direct Use Values
Indirect Use Values
Option Values
BequestValues
Existence Values
Direct consumption
• Food• Biomass• Recreation• Health
Functional benefits
• Ecological functions• Flood control• Storm protection
Future direct & indirect use values
• Biodiversity• Conserved habitats
• Habitats• Irreversible changes
Value of leavinguse- and non-use values for future generations
Value of knowledge of continued existence
• Habitats• Endangered species
Values decreasingly tangible
Use Values Non-Use Values
Alternative definition of TEV
Direct Use Values
Indirect Use Values
Option Values
BequestValues
Existence Values
Use Values Non-Use Values
Direct consumption
• Food• Biomass• Recreation• Health
Functional benefits
• Ecological functions• Flood control• Storm protection
Future direct & indirect use values
• Biodiversity• Conserved habitats
• Habitats• Irreversible changes
Value of leavinguse- and non-use values for future generations
Value of knowledge of continued existence
• Habitats• Endangered species
Values decreasingly tangible
Classifications of TEV
• TEV of an environmental good and service to an individual can be classified according to– the user (use by self – use by others or not
used at all)– the use (use by self or others - never used by
anybody)– the time of use etc.
• How does this correspond to the classification of direct and indirect valuation?
Contingent valuation
• Revealed preference methods can only estimate the use value of the environment, and only if that value affects behaviour in a measurable and interpretable manner
• For the rest, we have to use either hypothetical markets or experimental markets (together: constructed)
• Experimental markets have delivered little estimates (but a lot of insights), so the contingent valuation method remains – this is a stated preference method
Contingent valuation (2)
• Interview people, ask them for their WTP or WTA for the environmental amenity of interest
• Advantage: Applicable to more than direct use value
• Disadvantage: Hypothetical, people are unfamiliar with the situation, all sorts of biases may occur, interview design is always hard
History• First applications in early 1960s to value outdoor
recreation• 1979 the Water Resource Council recommended CV
as one of 3 methods to determine project benefits• In the mid 1970s the EPA funded a research
program to determine the promise and problems of the method
• The Reagan Executive Order 12291 (1981) – All federal regulations on environmental policy should be
submitted to a Cost-Benefit Analysis
• 1989 governmental decision on legitimacy of non-use values for TEV and equal standing
• 1989 Exxon Valdez oil spill – value loss of non-use values for US citizens
Theoretical foundation• Constructed markets can directly obtain WTP or
WTA, the preferred Hicksian welfare measures– Other techniques obtain measures of the Marshallian
consumer surplus
• Consider an improvement in environmental quality and the WTP for it
• Respondent gives the difference between the two expenditure functions
• WTP is defined as the difference between the two terms
0
0 0 0( , ; , ) ( , ; , )
i
i
M M
e P q U X e P q U X
Estimating WTP and WTA
• For n respondents this produces a set of welfare measures Wi(i=1,…,i,…,n) where Wi is either WTP or WTA
• Estimating the WTP or WTA amount– Based on sample mean for W– Based on sample median for W– Based on -trimmed mean estimators with =0.05 or
=0.10 – Regress responses on income and other socio-
economic characteristics to obtain a bid function
• Aggregate across the total population to derive the total value figure
* * * *( , ) or ( , , )i i i i iB B M S B B q M S
WTP vs WTA• People view gains and losses differently
– WTP is limited to an individual‘s income– WTAC is unbounded
• Confirmed by empirical studies, but not uncontested• Implies that surveys, policies need to be carefully
designed • If an individual has the legal right, WTAC is the
appropriate concept• It can be difficult to determine property rights
(public goods)• Sometimes the current allocation is taken as the
legal entitlement– Improvements = WTP and reductions = WTAC
Design a CV study
• Define a market scenario• Choose an elicitation method• Design market administration• Design sampling• Design of experiment• Estimate WTP-function
Define market scenario
• What is being valued? A day at the beach, a view of the beach? Pollution of a single beach, or all beaches?
• What is being valued is a policy intervention or a change in pollution – these have to be plausible and comprehensible
• What is the payment vehicle? A tax, an entrance fee, a levy on parking – note that people have opinions on these
Choose elicitation method
• Direct question: How much are you willing to pay?
• Bidding game: Are you willing to pay X? If yes, X+d? If no, X-d?
• Payment card: Choose from a list of numbers, including comparisons
• Referendum choice: Are you willing to pay X? for different X, to many people
• (Note: we are looking for the maximum amount)
Example: Payment card
Source: R.T. Carson (1991)
Administration & Sample
• Mail: No feedback or clarification possible
• Telephone: Has to be simple and short, no graphical material
• In-person: Expensive, interviewer bias• Are the people approached a
representative sample? And those who answered? Does the survey itself induce a bias, for example, in knowledge?
Experiment & Estimation
• If one hypothesizes a relationship between WTP and income, then the suggested values (payment card, bidding game, referendum) have to be independent of income
• If one hypothesizes a relationship between WTP and political colour, then one should include a question about the interviewees political opinions
• But sample sizes need to be small, and interviews short!
Validity• Content (face) validity: Does what is
measured and what is supposed to be measured coincide?
• Criterion validity: Do the measured values correspond to other measurements of the same thing?
• Construct/convergent validity: Do the measured values correlate to measurements of similar things?
• Construct/theoretical validity: Do the measurements correspond to predictions?
Reliability
• The more familiar people are with the good and the scale, the more reliable the measured values
• For public goods, referenda and taxes are perhaps best; for (quasi-)private goods, individual questions and entrance fee may be better
• The payment vehicle may distort the measure
• Payment cards and perhaps bidding games give the most reliable results
Potential Biases• Incentive
– Strategic– Compliance
• Implied value– Starting point– Range– Relational– Importance– Position
• Misspecification– Theoretical– Amenity– Context
Incentive Biases
• The interviewee deliberately gives a false answer
• Strategic bias: Influence the outcome• Compliance/sponsor bias: Comply with
presumed expectations• Compliance/interview bias: Try to
please/impress the interviewer• Protest votes: Interviewees may object
to valuation per se, or to being interviewed
Implied Value Biases
• Starting point bias, in the bidding game• Range bias, in the payment card• Relational bias, if examples of other
contributions are mentioned• Importance bias: The fact that the
interviewer bothers to ask ...• Position bias, if multiple goods are
valued
Misspecification Biases -Context
• Misspecification of the market scenario• payment vehicle• property right: WTP/WTA• method of provision: like payment vehicle• budget constraint: ability to pay• elicitation: maximum WTP?• instrument: survey may confuse
interviewees• question order
Other Misspecification Biases
• Theoretical• Amenity/symbolic: The perceived good
is different than intended• Amenity/part-whole: The interviewee
thinks the good is wider or narrower than intended (geographical, issue, policy)
• Amenity/metric: Different measurement• Amenity/probability: Different
assessments of the chance of delivery
Example: Drinking Water in Seoul
• A: Interviewer introduction– Explain the purpose of the survey– Indicate that the interview takes less than 30
minutes
• B: Background– Opinion about current tap water quality (very good,
good, average, bad, very bad)– Measures the household has taken in the last five
years to improve water quality (installed water filter, purchased bottled water, boiled tab water regularly, gone to a spring)
– Monthly household net income (show card if refuses to answer)
Drinking Water in Seoul (2)
• C: Value of water quality– Describe major pollution accident in 1991– If no action, how likely is a repetition?– Describe pollution prevention system– What is the maximum your household would
pay in increased monthly taxes for the goal attainable with the new monitoring system?
• D: Socio-economic characteristics– Age, highest level of education, number of
household members, average monthly water and sewer bill