2281AES Economics and Natural Resources

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2281AES Economics and Natural Resources

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Title: 2281AES Economics and Natural Resources


1
2281AESEconomics and Natural Resources
  • Module 10 Economic Valuation of Environmental
    Costs and Benefits Household Production
    Function
  • Lisa Alder

Water Science and Technology Board (2004) Valuing
Ecosystem Services Toward Better Environmental
Decision-Making
2
TABLE 1 Classification of Valuation Approaches
3
Definition
  • Consumers often gain utility not directly from
    the goods that they purchase
  • Instead they transform the goods by a household
    production function HPF into something that they
    value (Becker and Lancaster mid 1960s).

4
HPF Composition
  • Some form of modeling of household behavior
  • Assumption of a substitute/complementary
    relationship between the environmental good or
    service and marketed commodities consumed by
    household.
  • Constructed on the efficiency conditions
    marginal productivity of work at home equals the
    wage rate.

5
HPF Approaches
  • Allocation of time models for recreation or other
    activities involving household labor allocation
    (travel cost),
  • averting behavior models for health and welfare
    impacts of pollution, and
  • hedonic price models for the impacts of
    environmental quality on choice of housing

6
HPF Estimates
  • Important although ignored in national income
    accounting.
  • Estimated to account for 40 50 percent of the
    total production in Western countries, and in
    less advanced economies this fraction is
    presumably even higher (Bonke, 1992).

7
HPF Economic Theory
  • Early neoclassical models ignored productive role
    of households (treated all non labour time as
    leisure).
  • Mainstream economists (Mincer 1962, 1963 and
    Becker 1965) use New Home Economics and apply
    quantitative methodologies to household decision
    making.
  • Study of non market commodities and the
    associated allocation of household time now is
    part of economic theory

8
Early Measures of Utility
  • household utility is generated by commodities
    that are produced by combining the market goods,
    auxiliary goods, with time in a household
    production function (Becker 1965).
  • The outputs of this production process are the
    utility generating commodities.
  • market goods and time are not desired for their
    own sake but as inputs into commodity production.
  • All activities in household are productive.

9
Weaknesses
  • Focus on market prices, inputs and production
  • Severe lack of data.
  • Most of the inputs and the output are
    unobservable
  • Not usually possible to identify the models
  • The lack of information on specific household
    production inputs and production technology cause
    identification problems.

10
Gronau model
  • Later Gronaus model (1977) assumed consumption
    goods and commodities are perfect substitutes
    (work at home and in the market are perfect
    substitutes).
  • Direct utility is based on a persons indifference
    to the composition of the goods and services
    consumed (whether they are produced at home or
    purchased in the market).

11
Advanced Measures of Utility
  • In the Gronau model, a household maximizes a
    joint utility function subject to certain
    constraints considering the technology and
    resources.
  • The utility function derives from consumption
    goods, commodities produced at home, and leisure
    of the members of the household

12
Strengths
  • first to apply HPF to time allocation data
  • Successfully identified/estimated HP value
  • Reduced the complexity of identification of a
    household production technology by assuming
    perfect substitution between market goods and
    home produced goods.
  • analysed consumption patterns to yield amenity
    (non-use) values
  • Can be inexpensive to apply

13
Weaknesses
  • Requires detailed information on household
    expenditures using consistently defined
    consumption categories.
  • Amenity values are recovered from knowledge of
    market demands (demand-dependency)!!??.

14
HP and the Environment
  • Households allocates some labour, time and income
    for activities affected by environmental
    quality (state of the environment or
    goods/services it provides).
  • Household combine labour, environmental quality,
    and other goods to produce a good or service,
    for its own consumption and welfare (i.e.,
    household utility).
  • By determining how changes in environmental
    quality influence this household production
    function and thus the welfare of the household,
    it is possible to value these changes.

15
Valuing the Environment
  • Underlying Assumptions will vary depending with
    environmental problem and valuation approach.
  • all applications of the HPF approach use
    derivation of derived demand for the
    environmental asset in question.
  • Valuation of environmental quality can be
    extracted from information on the households
    purchases of marketed goods.

16
General Production Function Models
  • Value the support and protection that
    environmental goods and services provide economic
    activity in a two-step procedure (Barbier, 1994)
  • The physical effects of changes in a biological
    resource or ecological service on an economic
    activity are determined.
  • The impact of these environmental changes is
    valued in terms of the corresponding change in
    marketed output of the relevant activity.
  • e.g. The biological resource or ecological
    service is an input to the economic activity -
    its value equated with its impact on the
    productivity of any marketed output.

17
Static and Dynamic Approaches
  • In static approaches, the welfare contribution of
    changes in the environmental input is determined
    through producer and consumer surplus measures of
    any corresponding changes in the one-period
    market equilibrium for the output (Barbier,
    2000).
  • In dynamic approaches, the ecological service is
    considered to affect an intertemporal, or
    bioeconomic, production relationship.

18
Coastal Wetland Example
  • a coastal wetland that serves as breeding and
    nursery habitat for fisheries could be modeled as
    part of the growth function of the fish stock,
    and any welfare impacts of a change in this
    habitat support function can be determined in
    terms of changes in the long-run equilibrium
    conditions of the fishery.

19
Discounting
  • Discounting of many environmental policy impacts
    is important as these impacts extend over long
    durations and the timing must be factored into
    any valuation analysis.
  • Discounting is the approach most commonly used in
    economic analysis to capture the timing of
    benefits and costs.

20
Two Types of Discounting
  • discounting as a means of weighing the utility of
    future generations differently from that of
    present generations (utility discounting) and
  • discounting as a means of weighing consumption
    (through benefits and costs) differently at
    different times (consumption discounting).

21
Weaknesses
  • Dealing with average consumption patterns it may
    be necessary to determine population-weighted
    variables for different countries or regions.
  • Many of the countries have highly uneven
    distributions of income and spending
  • Consumption patterns of countries is generated by
    a representative consumer.
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