valuation 1 - low priority Flashcards

1
Q

How are nonmarket benefits determined?

A

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

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2
Q

The nonmarket benefits of environmental protection

A

 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

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3
Q

Measuring benefits - consumer surplus

A

 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

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4
Q

How to determine consumer surplus

A

 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

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5
Q

Problem with WTA and WTP

A

 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

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6
Q

Explaining WTP/WTA Disparities - prospect theory

A

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

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7
Q

Explaining WTP/WTA Disparities - substitution

A

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.

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8
Q

Using WTA or WTP

A

 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

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9
Q

WTP/WTA Ethical Issues

A

 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…

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10
Q
A
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11
Q

Nonmarket benefits

A

inferring how much people would be willing to pay or accept for these benefits if a market for them did exist

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12
Q

The nonmarket benefits of environmental protection

A

 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

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13
Q

Consumer surplus

A

 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

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14
Q

two ways to determine consumer surplus

A

 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

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15
Q

Problem with WTA and WTP

A

 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

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16
Q

Explaining WTP/WTA Disparities - Prospect theory

A

 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

17
Q

Explaining WTP/WTA Disparities - Substitution

A

 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.

18
Q

Using WTP or WTA?

A

 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

19
Q

WTP/WTA Measures of Benefits: Ethical Issues

A

 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…

20
Q

Step 1 in measuring the benefits of pollution reduction

A

 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

21
Q

Epidemiological or animal studies - problems

A

 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

22
Q

Perceived Risk

A

 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

23
Q

Risk Aversion

A

 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.

24
Q

Measuring Benefits: Three Methods

A

 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

25
Q

Contingent Valuation

A

 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

26
Q

CV design in general - Framing

A

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?)

27
Q

CV design - Practicalities

A

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?

28
Q

Sources of Error in CVs

A

 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

29
Q

Is CV useful or useless?

A

 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