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Valuation 10: Ecological Footprints

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Title: Valuation 10: Ecological Footprints


1
Valuation 10Ecological Footprints
  • The critique
  • The alternative
  • Critique on the alternative
  • Avoidance costs

2
Last weeks we looked at
  • The neo-classical approach to the monetary
    valuation of environmental goods and services
    that are not traded on the market
  • We will look at two alternatives (ecological
    footprints avoidance costs)
  • The second is ducking the issue, the first
    challenges economic theory

3
The Critique
  • The neo-classical theory of value is built on two
    premises
  • Supply versus demand or relative scarcity
  • Human preferences or what people want
  • The implications are, of course, that absolute
    scarcity is irrelevant, as long as people do not
    care and that, if it does not matter to people,
    it does not matter
  • There are, of course, also operational
    objections, and misinterpretations

4
The Critique -2
  • Nordhaus once said As agriculture has a share of
    only 3 of GDP, the impact of climate change on
    agriculture in unlike to exceed 3 of GDP
  • Obviously, prices are a linear approximation
    around the current situation, and should only be
    used to evaluate relatively small policy
    interventions
  • Of course, policy is always tinkering at the
    margin

5
The Critique -3
  • Wackernagel and Rees raise the interesting point
    that if a resource stock falls, its price will
    increase, so that the total value stays the same,
    so that nothing is the matter apparently
  • The math apart, WR clearly confuse stocks and
    flows if a resource price rises, further
    degradation is valued more, not less

6
The Alternative
  • So, what do WR propose to do instead?
  • The Ecological Footprint!
  • Since its inception in 1995, the EF has become
    tremendously popular, partly because of the
    energy of WR and partly because it is a really
    simple indicator
  • There a number of similar indices that are less
    popular but try do the same thing, that is,
    derive a superindicator measured in physical terms

7
Il Orma Ecologica
  • 57 mln Italians drink some 15 mln tonnes of milk
    per year an hectare yields some 500 kg milk, so
    thats 0.5 ha/cap
  • They eat 26 mln tonnes of cereals, for which they
    need 0.2 ha/cap the energy this takes comes
    later, the pesticides and nutrients are omitted
  • They eat about 5 mln tonne of meat per year this
    takes 0.8 ha/cap this is not just an average
    over space, but also over time what about
    eating diary cows?

8
Il Orma Ecologica -2
  • 57 mln Italians use 29 mln tonne of timber, 26 of
    which is imported with 2 kg/ha, this take 0.25
    ha/cap
  • Wool .3 mln tonne, 15 kg/ha, so 0.3 ha/cap
  • (Note that math is really not their strongest
    point)
  • Italians consume 12 GJ of coal absorbing the
    emitted carbon at 55 GJ/ha would take 0.2 ha/cap
  • Finally, Italians have about 0.1 ha/cap of
    build-up area

9
Il Orma Ecologica -3
  • So, now we have ha/cap for agriculture, forestry,
    energy and living
  • We cannot just add these up, because agricultural
    land is biologically more productive than are
    forests (never mind that this is because of human
    disturbance and fertilizers)
  • Multiplying space with the appropriate
    indicators, Italians use 4.2 ha/cap
  • But, they have only 1.3 ha/cap!

10
Il Orma Ecologica -4
  • Italians use 4.2 ha/cap
  • But, they have only 1.3 ha/cap!
  • Note that the ecological footprint implicitly
    condemns international trade it states that
    Italy uses 3 times its allocated space, which is
    possible only because Italy forcibly uses other
    countries room
  • This point becomes even more pugnant if one
    calculates the EF for cities e.g., Londons
    footprint is 200 times the size of the city

11
Ecological Footprints (ha/cap)
12
Ecological Footprint
  • World consumption takes up about 2.8 ha/cap,
    whereas the world has only 2.1 ha/cap available
  • This is only possible because we are using up
    fossil resources which is true for energy, soil
    and water
  • This is a recipe for disaster, unless one
    considers that resource stock are being replaced
    with capital and knowledge stocks

13
Tols Footprint
  • My footprint is about 20.4 (34.5) hectare if
    everyone were to live like me, we would need 11.3
    (19.1) Earths
  • Although I am a vegetarian and generate little
    waste, I do live in a big house far away,
    commuting by car I also fly a lot
  • See the test on http//www.earthday.net/footprint.
    stm
  • This test may surprise you, shock you, or make
    you think, please remain calm ... But not too
    calm!!

14
Critique
  • The used weights are presumably physical and
    ecological and therefore have little relation
    to social or political priorities this may
    reflect a higher truth, but is not handy for a
    decision analytic tool
  • What to make of an assessment that praises
    Iceland and Indonesia, while condemning
    Bangladesh and Singapore?
  • Part of this comes from using world average
    productivity figures

15
Critique -2
  • Why are crop land and roads equally productive?
  • Why are all forests equal, regardless of how they
    are managed?
  • A large share of the ecological footprint is
    energy use which is converted to land by
    absorbing carbon in tree plantations why not
    biomass energy, or solar power? both would lead
    to substantially lower numbers

16
Critique -3
  • Ecological footprints are as arbitrary as the
    region to which they are applied
  • Computing an EF for a locality implicitly
    condemns trade and the good things that trade
    does for the economy and the environment
  • Most problematic, however, the EF has an absolute
    measure of value much like the classical labour
    theory of value

17
Critique -4
  • Most problematic, however, the EF has an absolute
    measure of value much like the classical labour
    theory of value
  • The labour theory of value found its grave, in
    theory as well as in practice
  • Absolute value theories may work as long as the
    anchor is indeed dominant, but get increasingly
    complex if that is no longer the case
  • Whether land dominates at present is, at best,
    questionable

18
The Use of Valuation
  • Valuation serves three purposes
  • First, we want to determine the optimal level of
    policy intervention
  • Second, we want to value the total amount of
    environmental pollution and degradation, e.g.,
    for inclusion in the national accounts
  • Third, we want to calculate the compensation
    polluters need to pay to victims
  • Some require marginal costs, others consumer
    surpluses (well, CV or EV)

19
Avoidance Costs
  • The avoidance cost method turns the first purpose
    optimal policy on its head
  • We know the (marginal) costs of emission
    reduction
  • We assume that the actual policy intervention is
    optimal
  • Therefore, we know the marginal benefit of the
    optimal policy
  • But, obviously, not the welfare change

20
Avoidance Costs -2
  • With a marginal benefit point estimate, we can
    meet the second and third purpose of valuation
    (national accounts, compensation)
  • But, not the first (optimal policy) the
    implicit assumption is that, even though the
    valuation specialist is incapable of estimating
    the marginal benefit curve, the policy maker is
    able to, although apparently unable to express
    this

21
Avoidance Costs -3
  • Note the difference with travel costs and hedonic
    pricing
  • In both methods, we assume that the consumer
    makes a trade-off between environmental amenities
    and marketed goods and optimizes that trade-off
  • However, we look at many consumers, so that we
    not only can estimate the marginal price curve
    but also average out randomness and errors
  • Avoidance costs is based on one decision
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