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Title: Review of last lecture


1
Review of last lecture
  • Hedonic pricing
  • Valuation of environmental amenities associated
    with property values
  • Effect of landfill sites on house values
  • Health risks morbidity and mortality
  • Market assumptions of hedonic pricing
  • Travel cost
  • Overview of travel cost
  • Practical considerations and limitations

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Choice modelling Tim Capon
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Lecture outline
  • Choice modelling
  • Comparison of alternative nonmarket valuation
    techniques
  • Application of nonmarket valuation in developing
    countries

9
Overview of choice modeling
  • Conjoint analysis (CA)
  • A number of indirect hypothetical methods, widely
    used by market researchers in the evaluation of
    new products and markets
  • Based on the premise that commodities can be
    viewed as bundles of various attributes (as with
    hedonics)

10
Overview of choice modelling
  • Respondents rank or rate a series of these
    bundles in which some or all of the different
    attributes are allowed to vary.
  • From these rankings or ratings, marginal rates of
    substitution between the different attributes can
    be estimated.
  • By including price as one of these attributes,
    these marginal rates of substitution can be
    translated into WTP for changes in the levels of
    each attribute.

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Choice modelling
  • Four stages
  • Identification of key attributes relevant to the
    choices of interest
  • Selection of scenarios (alternatives) that will
    be used in the survey
  • Actual survey
  • Modelling and analysis

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Attribute key
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Attribute levels
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Four different types of format
  • Dichotomous or contingent choice
  • Contingent ranking
  • Contingent rating
  • Graded pair or pairwise rating

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Dichotomous or contingent choice
  • Respondents are asked to choose their most
    preferred alternative from two or more choices
    with different levels of attributes
  • Dichotomous choice contingent valuation (Are you
    willing to pay or not?) is essentially a
    special case of dichotomous choice CA, where the
    study is limited to two alternatives the status
    quo and a price with a given level of
    environmental quality.

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Dichotomous or contingent choice
  • Relaxing these restrictions allows CA to
    emphasize tradeoffs among hypothetical
    alternatives over the purchase of an
    environmental amenity.
  • Some argue this change in emphasis deflects
    emotional stress, and as a result, is less likely
    to generate protest or symbolic responses.
  • Dichotomous choice CA has been used to estimate
    WTP to preserve different kinds of undeveloped
    land, to take recreational fishing trips,
    preferences for locating landfills, and for
    reducing health risks.

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Contingent ranking and rating
  • Contingent ranking asks respondents to rank a set
    of hypothetical alternatives from most
    preferred to least preferred.
  • Used to evaluate the demand for electric cars,
    WTP for improved visibility at national parks,
    and WTP for improved water quality
  • Contingent rating asks respondents to supply
    information about how much they prefer one bundle
    to another.
  • Used to estimate WTP for different attributes of
    salmon fishing and waterfowl hunting

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Graded pair or pairwise rating
  • Respondents are shown two alternatives and are
    asked to show their preference for one of the
    products by choosing a number within a set of
    numbers.
  • For example, respondents might be asked to choose
    from 1 to 7, where 1 represents the strongest
    possible preference for one good and 7 the
    strongest preference for the other good.
  • The exercise is then repeated with different
    hypothetical alternatives.

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Advantages of choice modelling over contingent
valuation
  • Respondents are not required to monetize
    environmental goods or services explicitly.
  • Respondents are generally more comfortable
    providing qualitative rankings or ratings of
    attribute bundles, which include prices, rather
    than dollar valuations of the same bundles
    without prices.

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Advantages of choice modelling over contingent
valuation
  • CA focuses on marginal tradeoffs between
    attributes rather than asking respondents to
    state a maximum WTP.
  • CA allows a more detailed evaluation of the
    alternatives.
  • Like dichotomous choice CV (referendum format
    question) CA is believed to present a more
    realistic, familiar setting for respondents.

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Advantages of choice modelling over contingent
valuation
  • Some researchers believe that the ability to
    accurately answer hypothetical questions about
    unfamiliar goods improves with reflection or
    examination of preferences.

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Advantages of choice modelling over contingent
valuation
  • Responding to a survey can be viewed as a dynamic
    learning process.
  • The greater number of elicited responses in CA
    may allow more room for learning to occur.
  • Potential tradeoff with people getting tired of
    answering more questions.

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A technical problem
  • A problem with all CA methods and the referendum
    versions of CV.
  • Because respondents do not directly give a WTP
    estimate for themselves there is an intermediate
    inferential stage in the benefit estimation
    process.

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A technical problem
  • This intermediate stage takes the yes/no, ranking
    or rating information from the survey, embeds it
    in an assumed structure of preferences and uses
    statistics to tease out the desired WTP answer.
  • The problem is that the final answer is quite
    sensitive to the choices made at each step of
    this process.

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Would you be willing to pay for an
environmental change?
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Percentage of respondents WTP each amount
  • If the Wi above are ordered so that
  • W1 lt W2 lt . . . lt WM
  • then we expect
  • P1 gt P2 gt . . . gt PM
  • subject to random response error and the
    systematic influence of such independent
    variables as income, education, and pre-existing
    environmental position.

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Statistical inference
  • The analyst faced with this data can choose from
    roughly a dozen methods for inferring the
    relationship between the probability of the
    respondent accepting the bid presented to her
    or him and the size of that bid.
  • The resulting relationship implies a mean WTP for
    the project or policy being asked about.
  • Then to complete the benefit side of the
    cost-benefit analysis, the inferred mean WTPs are
    multiplied by the number of individuals assumed
    to be fairly characterized by that number.

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Sewers and wastewater treatment
  • A project to improve water quality being
    considered for a Latin American country by one of
    the multinational lending agencies.
  • The aim of the project is to improve ambient
    water quality in a river flowing through a major
    industrial city.
  • The river regularly has periods of zero dissolved
    oxygen, with attendant problems of noxious smells
    over reaches within the city.

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Sewers and wastewater treatment
  • Much longer reaches of the river that have no
    recreational value at any time due to poor water
    quality.
  • Smell, turbidity, lack of aquatic life, and
    generally disgusting appearance
  • The WTP figures were sought by describing the
    project and its predicted effects on the rivers
    quality and then asking the respondent if he or
    she would be willing to pay an amount W1 that
    varied across the sample of people interviewed.

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Per-household WTP for the project
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Choice of method
  • The choice of method is not a matter of chance.
  • The analyst could choose a method of inference
    that would be most likely to give a high mean WTP
    estimate.
  • Conventional CVM may involve responses to direct
    questions about WTP and problems such as
    protests, ignorance and confusion but the
    responses once obtained do not have to be
    econometrically massaged.

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Blamey et al. (2000)
  • Valuing remnant vegetation in Central Queensland
    using choice modelling.
  • In the Desert Uplands region of Central
    Queensland, many pastoralists are clearing
    vegetation in order to improve cattle grazing
    production.
  • A choice modelling study was undertaken to
    provide estimates of the benefits of retaining
    remnant vegetation that are appropriate for
    including in a cost benefit analysis of tighter
    clearing restrictions.

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GM food
  • The results of the choice modelling analysis
    suggest that consumers require a discount on
    their weekly food bill before they will purchase
    GM food.
  • Gene technology using animal and plant genes was
    found to be more objectionable to respondents
    than that using plant genes alone, especially
    among women.
  • Age seems to accept preferences for a certain
    type of food, with older people generally more
    accepting of the use of gene technology.

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CV versus conjoint analysis
  • Stevens et al. (2000) found that when conjoint
    and CV questions differed only in rating and
    pricing format, respectively, WTP estimates were
    quite different.
  • Since most conjoint models essentially count
    maybe responses to valuation questions as yes
    responses, we conclude that conjoint model
    results often produce WTP estimates that are
    biased upwards.

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Direct vs indirect techniques
  • Indirect methods do not match the problem
    settings that need to be addressed.
  • Even if you try to combine the values from
    multiple indirect techniques underlapping and
    overlapping are unavoidable and not correctable
    even when only use benefits or damages are
    sought.
  • Nonuse damages or benefits are both real and
    ethically important, though where to draw the
    line around relevant nonusers will remain an
    enormously difficult question in any real
    situation.

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What about the problems of direct questioning
methods?
  • Problems such as the hypothetical nature of these
    studies and the limited knowledge and calculating
    abilities of respondents.
  • To answer these difficulties we need to know how
    much to inform respondents about unfamiliar
    problems before asking them questions.
  • Many of the biggest valuation challenges of the
    future are likely to involve problems where
    multiple dimensions can change more or less
    independently.

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Developing countries
  • Developed countries OECD countries
  • Organization for Economic Cooperation and
    Development
  • Developing countries
  • Any small selection from the roughly 125 to 150
    nations that might be called developing would
    fail to do justice to some dimensions of the vast
    range of physical and economic settings
    represented.
  • Typical country can be pictured as toward the
    poorer end of the income scale and as lying in
    the tropics with a large proportion of its
    citizens in subsistence agriculture

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Nonmarket valuation in developing countries
  • Useful case study of nonmarket valuation
  • Cost-benefit analyses conducted as part of
    development projects by international agencies
    such as the World Bank.
  • For example, the Interamerican Development Bank
    requires that all loan proposals include
    cost-benefit analyses.
  • E.g. wastewater treatment plant environmental
    benefits?
  • E.g. road or a dam side effects on the
    environment?

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Nonmarket valuation in developing countries
  • Developing countries have lower incomes, less
    recreation time, less access to transportation,
    poorer health status, more people in agriculture
    and a relatively greater role for resource
    extraction.
  • These differences imply that there may be
    corresponding differences in the relative
    importance of specific sources of (or routes to)
    benefits or damages.

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Types of environment problem
  • The type of environmental problems poor people in
    developing countries face has consequences for
    the type of nonmarket valuation methods that are
    appropriate.
  • Differences exist between the relationship to the
    environment between the rural and urban poor.

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Rural poor
  • the destitute are those who have very few
    assets, are marginalized, and who are continually
    forced to live from hand to mouth. They have no
    recourse but to exploit the environment around
    them, even if it means degrading its long-term
    value for their needs (UNDP 1999 27).
  • Heavily dependent on natural resources for their
    livelihoods.

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Rural poor
  • The pressure from population growth is expressed
    in territorial expansions or migration to an
    urban area.
  • The essential message here is that attacking
    poverty in rural areas is then necessarily a
    matter of improving poor peoples ability to
    derive sustenance and income from more productive
    sustainably-managed natural resources (UNDP
    1999 28).

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Urban poor
  • The urban poor live in densely populated regions
    often characterized by substandard housing,
    inadequate or polluted water, lack of sanitation
    and sold-waste systems, outdoor air pollution,
    and indoor air pollution from low-quality cooking
    fuels.
  • Under such living conditions, health risks are
    heightened because of the concentration of people
    and production.

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Urban poor
  • Many of the linkages between the urban poor and
    the environment occur in the form of the effects
    of the environment on them.
  • Urban growth often encroaches on farmland,
    destroys wildlife habitats, and threatens
    sensitive ecosystems and inshore fisheries.
  • Improving the environment in urban areas can
    reduce poverty because it improves poor peoples
    health.

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The value of natural resources in developing
countries
  • Probably the most important factor contributing
    to natural resource price distortion in
    developing countries is market failure.
  • Market prices in these regions do not take
    account of externalities.
  • For example, when lumber is exported from a
    country in SE Asia to Japan or France, the
    importing country will pay the prevailing market
    price, which is highly unlikely to include the
    environmental effects of the logging and the
    foregone benefits (use and nonuse values)

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Benefit estimation for the developing country
setting
  • Indirect or revealed preference connect the
    environmental benefit or damage to the market
    setting, find the necessary data and manipulate
    it in ways consistent with consumer theory and
    its own structure so the output is convincing.
  • Direct or stated preference ask hypothetical
    questions more or less directly about the
    environmental project, policy, or action of
    interest.

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Hedonic pricing
  • Based on the premise that a good or service can
    be defined as a bundle of characteristics or
    attributes that together determine the price of a
    good via the demand for and supply of the
    characteristics in the market for that good.
  • For example, the price of a residence can be
    viewed as a function of its size, age, physical
    condition, proximity to schools, quality of the
    environment etc

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Assumptions of hedonic pricing
  • The market involved (housing or labour) is
    assumed to be in equilibrium.
  • Needs to meet the assumptions for a market to be
    in equilibrium (see previous lecture on hedonic
    pricing)
  • Buyers and sellers are assumed to be aware, and
    to appreciate the effects, of the environmental
    quality characteristic(s) of interest.
  • There needs to be a sufficiently wide variety of
    choices that all combinations of characteristics
    are available in the market.

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Assumptions of hedonic pricing
  • All three assumptions seem less likely to be
    fulfilled in applications in developing
    countries.
  • Only a few favoured builders may be allowed to
    operate
  • There may be residence requirements that do not
    permit free movement around a metropolitan area
  • The awareness requirement seems less likely to be
    met because of the combination of lower
    educational levels, less environmental testing
    and regulation generally, and perhaps even
    control over the dissemination of sensitive
    information practiced by nervous regimes.

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Assumptions of hedonic pricing
  • Even where markets are well functioning and
    individuals well informed, data collection may be
    much more problematic in developing countries.
  • There is likely to be relative scarcity of
    monetary land and property transactions in many
    cultures. And those that do occur may not be
    recorded in a fashion required for economic
    analysis.
  • Because of these reasons there are few hedonic
    pricing studies and few hedonic wage studies in
    developing countries.

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Travel cost
  • Travel cost values a recreational site or
    characteristic by using the value of the time and
    other cost incurred in visiting the site as a
    proxy for what a visitor would be willing to pay
    to visit the site.
  • The focus of travel cost studies on recreational
    value in developing countries has been on
    international visitors and therefore of limited
    use, as most applications to actual decisions
    confine attention to domestic WTP for the project
    being analyzed.

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Travel cost
  • There is a different relationship between
    environmental quality and the recreational
    market in developing countries.
  • Where people are poorer and have less access to
    transportation, travel for any sort of recreation
    may be very limited.
  • As a result, travel cost may have limited use in
    estimating the domestic benefits of water
    treatment projects as they accrue via water-based
    recreational sites.

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Travel cost
  • This is because few national incur the kinds of
    travel costs needed for travel cost to generate
    valid WTP estimates.
  • The great majority of travel cost studies value a
    recreational site as it exists.
  • Valuing the introduction of a new site or
    proposed changes to an existing site, as would be
    required for analysis of a water quality
    improvement project, requires more sophisticated
    versions.

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Contingent valuation
  • The application of contingent valuation in
    developing countries is fairly new.
  • The difficulties in applying revealed preference
    methods, particularly in estimating demand for
    water supply and sanitation, mean that
    hypothetical methodologies are now seen to enjoy
    an advantage over indirect methods in developing
    countries.

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Contingent valuation
  • Can be used to address almost any policy question
    asked.
  • Can measure use and nonuse values.
  • Also, it may be easier to conduct contingent
    valuation surveys in developing countries than it
    is in developed countries.
  • Higher response rates, with respondents receptive
    to listening and answering the questions posed
  • Interviewers are relatively inexpensive to prices
    in industrialized countries
  • Allows CV researchers to use larger sample sizes

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Challenges to using CV in developing countries
  • Many developing countries may be only partially
    monetized, causing difficulties in translating
    values into monetary terms.
  • Might use volumes of rice or grain instead.
  • Need to translate the survey instrument into
    local languages or dialects.
  • Considerable attention must be paid to local
    institutional and cultural issues.

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Challenges to using CV in developing countries
  • The survey designers must be sensitive to the
    attitudes of local people and their perceptions
    about local, national and international
    institutions.
  • Focus groups are a useful way to learn which
    payment vehicle, funding, and service delivery
    mechanism CV survey respondents are likely to
    trust.

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