valuation 1 - low priority Flashcards
How are nonmarket benefits determined?
Nonmarket benefits are determined by inferring how much people would be willing to pay or accept for these benefits if a market for them did exist
The nonmarket benefits of environmental protection
Use: value in use
Option: a resource has option value if the future benefits are uncertain and resource depletion is irreversible
Existence: value from the existence of a species/resource
Total Value = Use + Option + Existence
Measuring benefits - consumer surplus
The benefit measure for pollution reduction is the increase in consumer surplus due to such a reduction
Consumer surplus is the difference between what one is willing to pay and what one actually has to pay for a service or a project
How to determine consumer surplus
Willingness-to-pay (WTP) for improved quality
Willingness-to-accept (WTA) compensation in exchange for degraded quality
In theory, because income differences are small, WTA should be only a bit higher than WTP
Problem with WTA and WTP
WTA values are typically 2 to 7 times as high as WTP values!
This difference persists even in tests specifically designed to control for inflated WTA figures
Explaining WTP/WTA Disparities - prospect theory
Prospect theory: people may adopt the status quo as their reference point and demand higher compensation to allow environmental degradation than they are willing to pay to make improvements -otherwise known as the ‘endowment effect’
If prospect theory is correct, it would reshape our marginal benefit curve for pollution reduction
Explaining WTP/WTA Disparities - substitution
Substitution. The degree of substitutability between environmental quality and other consumption goods
If environmental goods really have no good substitutes this could explain the difference.
Using WTA or WTP
The standard practice is to use WTP because WTA estimates may be less reliable
But if we think of common property as belonging to “the people” then WTA maybe the best measurement
WTP/WTA Ethical Issues
With either WTA or WTP, the use of consumer surplus as our benefit measure automatically leads to higher benefits for clean-up in wealthier communities.
The rich will both be willing to pay more for clean-up, and also require higher levels of compensation for degradation.
This is especially stark when we come to putting a value on reduced risk of death: one of the most important benefits of environmental clean-up…
Nonmarket benefits
inferring how much people would be willing to pay or accept for these benefits if a market for them did exist
The nonmarket benefits of environmental protection
Use: value in use
Option: a resource has option value if the future benefits are uncertain and resource depletion is irreversible
Existence: value from the existence of a species/resource
Total Value = Use + Option + Existence
Consumer surplus
The benefit measure for pollution reduction is the increase in consumer surplus due to such a reduction
Consumer surplus is the difference between what one is willing to pay and what one actually has to pay for a service or a project
two ways to determine consumer surplus
Willingness-to-pay (WTP) for improved quality
Willingness-to-accept (WTA) compensation in exchange for degraded quality
In theory, because income differences are small, WTA should be only a bit higher than WTP
Problem with WTA and WTP
WTA values are typically 2 to 7 times as high as WTP values!
This difference persists even in tests specifically designed to control for inflated WTA figures
Explaining WTP/WTA Disparities - Prospect theory
Prospect theory: people may adopt the status quo as their reference point and demand higher compensation to allow environmental degradation than they are willing to pay to make improvements - otherwise known as the ‘endowment effect’
If prospect theory is correct, it would reshape our marginal benefit curve for pollution reduction
Explaining WTP/WTA Disparities - Substitution
Substitution: The degree of substitutability between environmental quality and other consumption goods
If environmental goods really have no good substitutes this could explain the difference.
Using WTP or WTA?
The standard practice is to use WTP because WTA estimates may be less reliable
But if we think of common property as belonging to “the people” then WTA may be the best measurement
WTP/WTA Measures of Benefits: Ethical Issues
With either WTA or WTP, the use of consumer surplus as our benefit measure automatically leads to higher benefits for clean-up in wealthier communities.
The rich will both be willing to pay more for clean- up, and also require higher levels of compensation for degradation.
This is especially stark when we come to putting a value on reduced risk of death: one of the most important benefits of environmental clean-up…
Step 1 in measuring the benefits of pollution reduction
Step 1 in measuring the benefits of pollution reduction: assess the risks
Information on health risks come from two sources:
Epidemiological: studying past cases of human exposure
Animal studies from laboratories
Epidemiological or animal studies - problems
Epidemiological studies: expensive, uncommon and hard to do well.
Animal studies: require translating information from high-dose animal studies to low dose human exposure, creating multiple uncertainties
Perceived Risk
Individuals may perceive risk differently than the actual risk for a few reasons:
Voluntary vs involuntary risk
Lack of knowledge
Distrust of Experts
People are risk averse
Risk Aversion
Risk aversion: people dislike exposure to catastrophic events occuring w/ low probability more than unpleasant events occurring w/ high probability– even if they have the same average cost.
Measuring Benefits: Three Methods
Stated Preference: value of benefits obtained from survey methods
1. Contingent Valuation Analysis
Revealed Preference: value of benefits inferred from observed market data
2. Travel Cost Analysis
3. Hedonic Regression Analysis
Contingent Valuation
Survey methods used by economists to determine the benefits of environmental protection; the survey responses are “contingent” upon the questions asked
Basically, ask people their WTP and/or WTA
CV design in general - Framing
Set up a ‘hypothetical market’ – this ‘frames’ the issue. E.g. policy restoring old civic buildings. Reason for payment (aesthetic improvement) must be clear; as must the means of raising funds (raising taxes). Pre-testing of questionnaires (focus groups?)
CV design - Practicalities
Face-to-face/telephone/mail - potential biases? non-response bias, interviewers ‘leading’ respondents…
Bids obtained through detailed explicit choices, open-ended questions, or dichotomous choice?
Sources of Error in CVs
Hypothetical Bias
Hypothetical questions → hypothetical responses
Free-riding
May lead understatement of true WTP
Strategic Bias
People might inflate their WTP to achieve greater clean-up if they believe they will not have to pay their WTP
Embedding Bias
Answers are strongly affected by the context provided about the issue at stake
Is CV useful or useless?
Economists disagree about the reliability of CV analysis. Also doing a ‘state of the art’ job can be very expensive - see Diamond and Hausmann (1994)
However, CVs provide the only available means for estimating the existence value component of nonmarket benefits, so they are often used