Professor Urs
Luterbacher and Dr. Ellen Wiegandt, with the participation of Professor Richard
Blackhurst
Oil shock of the 1970’s:
awareness in resource problems. Green parties beginning 80’s. In the last 15
years, public, scientific and academic interest in environmental issues has
increased. Evidence: World Climate Research Program, Geneva; Convention on
Bio-Diversity; Intergovernmental Panel on Climate Change with three Assessment
Reports so far (1990, 1995, 2001), the latest forecasting a temperature rise of
up to 5.7 degrees until 2100. There is now a strong consensus that climate
change is partly induced by human activity.
Renewed interest in global
environmental problems was sparked by ozone depletion discovered in the
middle of the 80’s. Fast political response: Montreal Protocol (1987).
United Nations
Conference on Environment and Development (UNCED) in Rio (1992). Framework Convention
on Climate Change (FCCC). Stabilize Greenhouse Gas emissions to a sustainable
limit. Kyoto protocol: binding limits for Annex 1 countries (industrialized
countries), not binding for developing countries. However, the Parties could
not agree on how to implement these targets (question of tradable permits,
carbon sinks, cooperation with developing countries, etc.) at successive COPs
in Buenos Aires (1998), Bonn (1999) and The Hague (2000).
Humans have always
interacted with their environment. But today’s problems are more global, and so
have to be their solutions.
Social
system Natural system
Industrialization Climate
Change
Trade
Demography
1500 –
1850: Cooling down of continental Europe; only Inuit’s were able to survive in Greenland.
“Modern agriculture” disappeared. Society had time to adapt institutions (but
didn’t do it in this case). In other cases, adaptation has to be fast (e.g.
deforestation of the Amazon).
Human
influence on climate is complex: unevenly divided rise and fall of sea levels
and rise in temperatures (Europe colder in the short term), enhancement of the
water cycle (precipitation) à turns of water change; extreme events. Models
can give very different results when different assumptions are made.
We live in an
unsustainable way:
à Tietenberg (1992). Environmental and
Natural Resource Economics.
Basic pessimist model: Humans clash with environment, not in control
1) Run-out of non-renewable resources, collapse of
economic system
2) Piecemeal approach not able to solve problems
3) Immediate limitation of population, pollution and economic growth necessary
Characteristics:
Exponential growth vs. fixed supply; positive feedback loop.
Basic optimist model (Kahn, Boserup, Simon, Tietenberg): Humans
rich and in control of environment
1) Population growth = S-shaped curve (induced by
scarcity)
2) Economic growth: most better off; interference unethical
Characteristics: Productivity
rises more than food demand (technology change, also induced by scarcity;
Boserup and Simon)
Environment – economy =
closed system (resources, waste)
·
Static efficiency (no time factor): demand curve, opportunity
cost; marginal cost = marginal benefit; net benefit maximization
·
Dynamic efficiency (time factor): Static efficiency
& timing. Marginal net benefit period 1 = marginal net benefit period 2 (discounted).
Discount rate: the higher the less value is given to future consumption. A
resource market is dynamically efficient when the present discounted value
(PDV) of total surplus is maximized.
à Sustainability: Criterion (Rawls) = future generations at least not
worse off than current generation. Dynamic efficiency can satisfy this
(saving for future generations).
Common pool resources
included in collective goods.
Unrestricted
access Restricted
access
Non-exclusive (problem: “free rider”) Exclusive
(“club good”)
Indivisible (consumption à same amount) Divisible
(consumption à reduces amount)
Pure
public good: e.g. TV; no
rivalry in consumption. Rivalry: Consumption reduces benefits to others.
à Taylor (1987), The Possibility of
Cooperation
Problem
of collective action, Olson. Smaller group can organize itself and
profit more directly and more extensively than larger group. Cost of
organization / person vs. expected benefit / person.
Critique:
-
Size effect not so simple (Taylor); correlation size – privileged group weak
(Hardin)
- Static analysis (Taylor)
- Origin of cooperation not explained
PD = 2 actors, 2 dominant strategies. N person’s PD = tragedy of the commons. Hobbes vs. altruism.
Trade
= PD problem because of possibility of retaliation (Pareto-optimum: optimal
tariff)
Pool of fish = Chicken problem because fewer or no means of retaliation
(Pareto-optimum: avoiding disaster!) à rational individual action can lead to
strictly pareto-inferior outcome
Solutions:
-
Spontaneous/internal: iterated chicken; no use of sanctions
- External: centralized or decentralized. Community, state. Also persuasion for
changing attitudes.
Private Property rights:
Effects of each individual’s action internalised (& benefits). But discount
rate might be high à private proprietor might knowingly destroy the
resource. à Also private property needs sanctions. (Norms without sanctions don’t
work) Sanctions = solution to collective action problem.
Luterbacher (2001), International
Relations and Global Climate Change
The Physical System: “Global Climate Change: What we know/don’t know”. Martin Beniston, University of Fribourg.
Greenhouse gases keep
atmosphere warmer. Too much of them means different systems are affected in a complex
way:
·
Atmosphere: warms
up
·
Cryosphere: Ice
caps melt; glaciers retrieve; snow reflects less light back
·
Hydrosphere: sea
level rise up to 1 m; availability of fresh water
·
Biosphere:
Vegetation changes; “moisture pump” (amount of precipitation); desertification
CFC’s 25% Refrigeration, sprays (Phasing
out since 1987) 200 ; 1 (lifetime, efficiency)
NO2 7% Burning
of fuels 150
; 280!
CH4 15% Rice fields, life stock (Big increase) 10
; 56!
CO2 55% Industry,
transportation, energy conversion, biomass burning (Increase) 80-140
HFC-42, even no not yet used on any noticeable
scale, also listed in the Kyoto protocol because of the efficiency of 490-9’100
Global Warming: Conclusions of the Third Assessment Report (TAR) of the IPCC, 2001.
·
Global average
surface temperature increased over the 20th century by about 0.6 C.
Rate and duration of warming in the 20th century much greater than
any century of the millennium. Likely that 1990’s = warmest decade of the last
140 years; and 1998 = warmest year of the millennium.
·
Temperatures have
risen during the past four decades in the lowest 8 kilometres of the
atmosphere.
·
Snow cover and
ice extent have decreased.
·
Global average
sea level has risen and ocean heat content has increased.
·
Emissions of
greenhouse gases and aerosols due to human activities continue to alter the
atmosphere in ways that are expected to affect climate.
·
Confidence in the
ability of models to project future climate has increased. Further action is
required to address remaining gaps in information and understanding.
·
“There is new
and stronger evidence that most of the warming observed over the last 50 years
is attributable to human activities” (SAR: “The balance of evidence suggests a discernible human influence
on global climate”).
·
Human influences
will continue to change atmospheric composition throughout the 21st
century
·
Global average
temperature is expected to increase by 1.4 to 5.8 C during the 21st
century
·
Sea levels are
projected to rise by 0.09 to 0.88 metres.
·
Anthropogenic climate
change will persist for many centuries.
All temperatures in the late 90’s represent temperature records in the last
1’000 years; warming between 10 and 100 times than “natural” warming
Very complex. Different IPCC scenarios with various
population growth, economic growth and policy assumptions.
Founded 1988 by WMO
and UNEP; 200+ scientists.
Signed in 1992, ratified by around 170 countries
Aim: protocol limiting greenhouse gases
Voluntary measures
Financial incentives
Carbon taxes: polluter pays principle
Joint implementation: buying your share of reduction
Reduction target of around 5% of the 1990
levels by 2012
à Necessity to act quickly; precautionary principle, other beneficial
side effects
à Grassl (1999). Global Climate Change.
Changing atmospheric
conditions & land cover change = largely anthropogenic
à IPCC (1995). Second Assessment Report.
“Discernable human
influence on climate”
Flexibility mechanisms
(ways to reach emission targets without trimming output)
Managing Environmental Risks and Uncertainties
Risk = outcome uncertain or several outcomes
possible
Uncertainty = lack of information; can be reduced through
learning (Stephens)
People have learned to
deal with risks due to nature and due to other human beings (the latter
involving decision-making anticipation)
Risk management:
Some uncertainty about
CC
Pascale: Believing in
God = infinite expected benefits; chances of existence low
Rio Declaration, 1992:
“Where there are threats of serious or irreversible damage, lack of full
scientific certainty shall not be used as a reason for postponing
cost-effective measures to prevent environmental degradation.”
Value: Average realization of an outcome
(destruction of house) x objective value (cost house)
Utility: Subjective evaluation of value. Risk-averse,
risk-neutral, risk-taking individuals.
Discount rate: Used to compute Expected Present Value (EPV).
High à value present; low à value future. Too high: environmental
destruction. Too low: too much investment in large projects such as dams.
à Social risks are managed with institutions, which
incorporate norms.
à Colin W. Clark (1990). Uncertainty in
Economics.
Decisions are taken on Expected
Utility Maximization
Human responses to risks
are direct (dams) and informal (institutions). Goal: reduce uncertainty.
Optimisation theory
(e.g. hunting group); either static or dynamic (decisions today also have
effects in future)
à Shackley et al. (1999). Adjusting to Policy Expectations in Climate Change Modelling.
Dealing with
uncertainty: Evidence that scientists' perceptions of the policy process do
play a role in shaping their scientific practices. Most scientists want to keep
discussion over flux adjustments within climate modelling community to avoid
adverse public reaction. Epistemic cultures amongst climate modellers.
à D.W. Stephens (1990). Risk and Incomplete
Information in Behavioural Ecology.
Risk vs. uncertainty.
Direct and indirect (institutions) action. Evidence: Risk-taking people violate
utility law.
Risk-sensitivity: Risk
in itself has a cost. Animals are risk avoiding but risk-taking if survival is
at stake. However, risk sensitivity over getting something vs. risk sensitivity
over delaying something à more likely to accept risk
Dynamic programming: optimal size dependent on level of hunger.
Scarcity: Something is said to be scarce when if, at a zero price, more is
wanted than is available. Scarcity makes choice unavoidable.
|
|
S-shaped line:
output B: maximal
surplus C: Available
resources just cover costs Between A and C:
scarcity rent exists |
If this is a common, the
tragedy of the commons will occur (over-exploitation)
If this is privately owned:
production at point B (marginal product = marginal cost)
Prevent TOC if not
privately owned: tax to drive up costs until B; or divide into lots/quotas
where I determine the amount produced; or arbitrarily limit production at level
B. But there is need for an institution to set rules and limit
production. Institutions incorporate norms that facilitate the use of new
technologies. But: social system must guarantee institution.
Institutions to prevent
excessive depletion, to show the “shadow of the future”, to monitor and
sanction, and to solve the problem of social costs.
Spatial distribution
(justice) and temporal distribution: How to do it in the most efficient way?
Uncertainties: size of
the reserve (water, fish); technology change; number of people that constitute
demand; preference
“Bundle of rights” and
obligations
If PR is poorly defined
or lacking, resource degradation may result (distribution, efficiency)
Standard economic
literature: well-defined
private property rules
à Tietenberg (1992). Property Rights,
Externalities and Environmental Problems.
If 1) sufficient demand,
unrestricted access will lead to over-exploitation; 2) scarcity rent is
dissipated
- Resource =
privately-owned (restricted access)
- Universal: all resources privately-owned; all entitlements completely
specified
- No ambiguity
- Exclusivity: all costs and benefits to the owner (will anticipate
effects of diminishing returns)
- Transferability
- Enforcement of rights
Assumption: market
mechanism; no transfer costs; no income effect
Externalities = secondary or unintended consequence (private
marginal cost < social marginal cost). Even when externalities are involved,
PR can be efficient. Efficiency problems: pay for not causing damage; or
pay for the damage. Some say it doesn’t matter which solution.
Other economists: It does matter who gets rights/duties
à Bromley (1992). Making the Commons Work.
It could be that PR are
not socially neutral.
Rule
1 A can’t build fence without B’s consent B protected
Rule
2 A may build fence but must
compensate B
protected à liability
Rule
3 A may interfere with B; B has to buy
off A A protected
Rule
4 B may stop A from building fence but
has to pay A protected à liability
Rule
5 A may not interfere with B under any
circumstances B protected à inalienability
Examples:
Forest in Niger; land in Thailand. Exogenous changes in population and market
opportunity were combined to make the common property resource more valuable.
But then scarcity made new property arrangements necessary.
Privatisation
of CPR made sense because:
à Heller (2000). Three Faces of Property.
Classical distinction
obsolete for Heller: private (PP) – common (CP) – state (SP)
Common Property: Everyone can use and no one may stop someone
else from use (no excludability)
State (collective)
Property: material resources
answerable to the needs and purposes of society as a whole. No privileges, but excludability.
Liberal Approach (Hardin): privatisation (alternatively:
close-knit group to avoid TOC)
Constructive
Approach (Anti-Commons) of Heller
Tragedy
of the Commons Tragedy
of the Anti-Commons
No
private owners Multiple
private owners
Each privilege to use No
one privilege to use
No one right to exclude Everyone
right to exclude
à When state creates new ownership rights
without
giving individuals full ownership
rights
(e.g. socialist systems; biotechnology)
Integrative Approach (Limited common): Limited group of owners à eco & soc benefit from cooperative use of scarce resource; ensuring
autonomy to individual members, who retain a secure right to exit (e.g. martial
property, trusts). à Limited access – limited purpose.
Definitional
Approach: thing-ownership;
“bundle of rights”
Coase (1960). The
Problem of Social Cost.
The Tragedy of the Commons Debate
Standard economic
argument (Tietenberg): CP à environmental degradation due to Tragedy of
the Commons (TOC). A legal framework is needed also for private property. The
problem of scale can be solved through two ways: either the state makes
an initial investment and enforces PR; or a firm (a form of CP) puts the
necessary capital together.
à Hardin (1968), Tragedy of the Commons.
In every individual’s
interest not to restrain himself from use of a resource. Result: every
individual worse off than if everyone would have restrained himself.
Assumption: finite
resources.
Herdsman, oceans,
pollution, national parks, etc. Solution: privatise or keep public property but
restrict access.
Common propriety: resource well defined bounds, well delineated
group of users; included users participate in extraction; rules exist; users
share joint, nonexclusive entitlement to the fugitive resource; users compete
for the resource; existence of a group of rights holders
Open access:
1) Lack of entry
restrictions
2) Lack of limitations on number of inputs that each user uses
BUT: Membership and
rules (Stevenson) à CP not such a bad thing; TOC can be avoided.
à Runge (1992). Common Property and
Collective Action in Economic Development.
In a village economy, common
property may work: Relative poverty, critically dependent on local agriculture
and natural resources, uncertainty of income streams. Free-rider problem can be
socially controlled in villages.
à Stevenson (1991). Common Property
Economics: A General Theory and Land Use Applications
Open access resource =
depletable, fugitive characterized by rivalry in exploitation
|
|
“Property” |
“Property” |
Open Access |
Open Access |
|
|
Private
Property |
Common
Property |
Limited User |
Unlimited
Users |
|
Group
limitation |
One person |
Members only |
Members Only |
Open to anyone |
|
Extraction
Limitation |
By individual
decision |
By rules |
Unlimited |
Unlimited |
- Well-defined bounds
- well-delineated group of users
- included users participate in extraction
- rules exist amongst users
- users share joint, non-exclusive entitlement
- users compete for the resource
- existence of a group of right holders
History of Property Rights
Viability of CP: Swiss
Alps. Mix of CP (pasture land, forest, water) and individual exploitation. Why
successful:
Better time/resource
management; possible to equilibrate difference between poor and rich.
Pre-Middle Age (before
14th century): PP dominant. Plague à drop in population à rise in resource per capita à rise in wealth. After plague, some
transformation to pasture land (less manpower, adjust better to demand).
Valleys: Need for irrigation (collective action) à maintaining CP; state used to create
necessary scale to build the canals.
No TOC because limit in the numbers of animals and users
à New rights (institutional arrangement) as a response to shift in
population
à Same would be required now because of a shift in climate
Exhaustible, Renewable and Sustainable Resources
What is an exhaustible
resource (for the mid-term future) depends on present knowledge (e.g.
oil reservoirs) and technology. So ER are a relative concept. There is also
endogenous (demand-driven) technology development.
The net price
(market price minus extraction costs) should increase exponentially with the
interest/discount rate. (Schelling). Price evolution is consistent with
i. Substitution possibility.
P(t)=P(O)ei
If present is valued
over the future, i is high.
If future is valued over
the present, i is small.
If the population is
big, i is bound to be high in order to consume.
HP = Competitive
resource-owners will deplete at a socially optimal way. Exploitation comes to a
standstill at some point. Market à maximum conservation.
r: rate of return of
resource. In equilibrium r = i optimal
Conservationists
Dilemma (Lambelet):
If i >> r à resource is transformed (high social discount rate)
e.g. deforestation:
income flow from agriculture >> income flow from forests. Problems:
agricultural or income subsidies, welfare, cost of PR enforcement or undefined
PR, prohibition of trade. Also natural phenomenon and the location of land can
drive land use change.
Implications of land use change for climate change: reflectivity (albedo),
carbon sink, hydrology
If i << r à resource is underused; more tendency to find oil
HP only valid if
à Monopoly can deal with these assumptions.
Monopolist = conservationist’s friend
à Lambelet (1995). A Note on the Issue of Exhaustible
Resources.
Technological progress
can’t always solve the scarcity problem. Extraction = economic process;
costs per unit of extraction go up (e.g. gold mines).
Being careful with recycling:
entropy (process of degradation); energy used.
If extraction rate = i à indifference
Problem with HP:
production externalities à overexploitation (e.g. underground reservoir);
uncertainty; environmental externalities: not all costs internalised (extraction
costs too low); no perfect competition in these sectors. Monopoly à slower extraction
If SDR = 0 then Q = 0
à Maybe information gathering and dissemination of trends is enough for
authorities
à Tax on energy is bad; tax un undesirable by-products of
energy is good (CO2, SO2,)
à Schelling (1994). Intergenerational
Discounting.
Discount rate:
1) “Time preference”, postponing consumption
2) Lower marginal utility of consumption (higher
average future consumption)
Depends on:
- Rate of growth of consumption/capita
- Elasticity of utility with respect to consumption
1) “Impatience” only
applicable to individuals. Here about re-distribution of income/consumption
into future
2) Transferring income from poor (now, lower consumption) to rich (later,
higher consumption). Reason: Resource grows in transit.
à Need to apply “target efficiency”, either CO2 abatement (tax) or public
investment. Choice made according to efficiency.
à Solow. Sustainability: An Economist’s
Perspective.
Sustainability = distributional equity present – future
Sustainability = moral obligation to conduct ourselves
so that we leave to the future the option or the capacity to be as well of as
we are now
Obligation of
sustainability not represented in markets (discount rate: 5-6%); role of the
state: policy actions, taxes, subsidies, regulations.
à Fungibility of inputs and resources: we don’t “owe” the future a particular
thing; general capacity to create well being (can also be knowledge).
à Current environmental protection only contributes to sustainability if
it comes at the expense of current consumption and not investment;
directing rents on non-renewable resources in investment, particularly
environmental investment.
à The poor prefer consumption today
Population
The argument that simply
the number of people is the problem is more complex. Rwanda and The Netherlands
have about the same land / capita ratio.
à Lee and Tuljapurkar. Population Forecasting
for Fiscal Planning.
Dynamics of population
measurement for social problems (predictive numbers).
As a base: a static
evaluation of current population. Totals, age groups, space distribution.
Difficult and problematic: sometimes categories not comparable internationally.
Malthus (1798) studied the relationship between birth,
death, and marriage as well as the population – environment link. He held that
one couldn’t escape population pressure against the ceiling of resources.
Assumptions:
The exponential population
increase brings diminishing returns à limited access to resources à higher mortality
Pre-industrial people controlled population through:
There is also the influence
of high mortality.
à Not possible to project that to the present
à Birth-spacing necessary (Lestaeghe)
Fertility: controlled within families. Nuptiality (%
of people who are unfortunate enough to get married): controlled by institutions.
Linkage family – institution properties.
Malthus: only through mortality.
Population change endogenous, technological change exogenous (diminishing
returns). Reality: Shifts in technology.
Ricardo: Micro-sight of population increase: TOC with
childbirth
Malthus & Ricardo:
long-term wage = subsistence minimum
Pre-industrial
societies: High mortality,
high fertility
Malthus: Adapt age
of marriage, population can react, acceptable level. For this period, his
theory works quite well. However, he leaves out technology and doesn’t
explain shifts in demographic regimes.
Industrial societies: Low mortality, low fertility
Malthus: Can’t explain
how we got there. Reality: control by marriage; context of control (behaviour)
Simon: More people à faster technological change
Population change: exogenous. Technological change = endogenous. Growing
population à need to feed, wages go up, etc. Pressure on
people acts as incentive for technological development.
Sustainable development
in a finite world à no problem
Replacement scheme:
Africa 5.8; Europe 1.6; North America 2.1. Optimal: 2
Why the African trend?
Lestaeghe:
à High fertility rate
Some control in Africa:
long lactation, gap of sexual relations between birth and next act, diseases.
à Cultural norms are difficult to change – even with influx of
technology. In some parts of Africa, fertility is even on the increase. Western
culture: some “taboos” are lost.
à Boserup system doesn’t work in Africa
à Disease, ethnic conflicts, and – most importantly – AIDS à life expectancy down (Malthusian type of phenomenon)
à Lestaeghe (1986). On The Adaptation of
Sub-Saharan Systems of Reproduction.
Today, Malthus is not
sufficient: Technology (as a result of culture or of population
pressure) needs to be taken into account.
Demographic transition
from high fertility and high mortality to low fertility and low mortality has
happened in Western Europe. Latin America and Asia are in transition now. But
sub-Saharan Africa corresponds more to Malthus: population grows and food
production fall à widening gap. Neither technological adaptation
nor other checks of population seem to be found
à Need of fertility control; supportive spacing without interfering with
lactation; local institutions must play a greater role
à Simon (1986). Theory of Population and
Economic Growth.
Population growth has
effects on: consumption, production, public facilities, age-distribution.
Relationship of
additional people to given territory: additional knowledge à additional technological development
|
|
Waste remains
within national borders |
Significant
amounts of waste cross (exit) national boundaries |
Production
|
I |
III |
|
Consumption |
II |
IV |
|
|
Competitiveness
concern |
Use trade policies
to make MEAs more effective |
1971 GATT committee on environment (EMIT), never
convened until beginning 90’s
1995 Committee
on Trade and the Environment (CTE);
Good job in educating delegates; but no consensus due to the North-South
Divide;
Problems:
- Amend GATT to provide for MEAs? Environmentalists: MEA > WTO; developing
countries WTO < MEA
- Should the rules be revised in order to explicitly allow for PPM discrimination?
Industrial countries divided; developing countries against
Two main functions:
à Anderson and Blackhurst (1992). The
Greening of World Trade Issues.
More recognition that trade
plays a role in environmental problems through its effects on the volume and
location of economic activity.
Free trade improves
welfare if accompanied by optimal environmental policy. Liberalization of coal
and food à economic and ecological gains. Ex. food: raise incomes of LDC’s (more
exports), raise average incomes of IC’s (lower prices); less chemicals used to
pollute air, soil and water; increase in chemicals in LDC’s relatively less
important than reduction of these chemicals in IC’s. But forest may be
cut à empirical studies: land area for agriculture not very responsive to
price changes.
1st best
policy: attack environmental problem at source (e.g. pollution tax). 2nd
best policy: Trade measures (e.g. export tax).
à If externalities not accounted for, trade liberalization may
bring environmental damage.
Problem of missing
markets: Disputed, ambiguous or non-existing property rights. 1st
best policy: multilateral cooperation. Trade policies can bring about the degree
of multinational cooperation necessary to deal with transboundary EP. But:
efficiency of trade measures?
PPMs: Fear that discrimination based on PPMs is
unfair to competitors.
Effects of standards
on developing countries: If
POOR exports a product that RICH decrees higher environmental standards on,
POOR wins because of the terms of trade effect that higher prices bring. If
POOR imports a product that RICH decrees higher environmental standards on,
POOR looses through the TOT effect.
A polluting country that
damages the country to which it exports its goods may raise its
welfare by raising environmental standards (TOT effect).
à International competition in pollution-intensive industries combined
with appropriate environmental policies that correct market failures.
CO2-reduction: direct
costs (cost of tax), indirect costs (distributional effects)
à If resources correctly priced, trade liberalization benefits the
environment through a more efficient allocation of resources
Sometimes trade is the only
possibility to address environmental problems.
Where to tax? Depends on location of where pollution falls.
The victim country may be worse off through setting an optimal tariff
(TOT).
à Possible to reduce welfare in B by polluting B less, even no world income
rises à TOT gain resulting from tax
à Distributional effect
à Chichilnisky (1994). North-South Trade and
the Global Environment.
Differences in property
rights create a motive for trade among otherwise identical regions. South =
ill-defined property rights on environmental resources; trade makes overuse
worse.
“Pollution haven”
hypothesis not correct. Distinction between apparent (stirring from property
regime) and real comparative advantage.
Taxes in the South may be ineffective because
consumption demand is inelastic to price.
Trade and Environment: Production and Processing
Methods (PPM)
PPM = process and production methods; generally aim
to reduce or control negative externalities either originating during the
production processes or transmitted by products; before the product gets to the
retail stage
Product standards (“product-related PPMs”, Charnovitz) =
intended to deal with consumption externalities in the country of destination à GATT/WTO accepts legitimacy (see TBT Agreement)
Process standards (“non-product related PPMs”) = intended to deal
with the production externalities in the country of origin. à great controversy amongst WTO members (outside TBT Agreement)
PPMs can address:
à OECD (1995). Further Analysis on PPM: Trade
Measures and Alternatives.
Whether PPM-based trade
measures are OK should be analysed according to feasibility, effectiveness
and efficiency. In certain cases (shared resources, global
concerns), PPM-based trade measures may be effective when trade itself impedes
an MEA’s goal.
à Marceau (1999). A Call for Coherence in
International Law – Praises for the Prohibition Against “Clinical Isolation” in
WTO Dispute Settlement.
Need for coherence
within multilateral trade system; and between trade, development and
environmental policies.
Article XX: Recognition
of tensions between market access rights and other legitimate policies (such as
environment). Also SPS and TBT Agreements. Dispute settlement panels narrow
interpretation.
Tuna Dolphin: PPMs not allowed.
Gasoline case: Against environment.
Shrimp-Turtle: PPMs considered as Article XX exceptions, but
found not conform to chapeau of XX (unjustifiable discrimination).
à PPM issue not clear
à MEA/GATT issue not clear
Solutions: Guidelines
and Prescriptive Decisions, waivers, formal interpretation by the General
Council, Amendment of WTO Agreements (e.g. DSU), An Understanding, Plurilateral
or Multilateral Agreement, World Environment Organization.
à Charnovitz (2000). Solving the PPM Puzzle.
PPMs are not excluded per
se (see Shrimp-Turtle) by case law, but distinction:
Sometimes trade measures
good 2nd best policy to address the problem of free riders, and/or
if international cooperation is not possible.
Migration
Migration is linked to
the environment in 2 ways:
1) Change in environment (drought, etc.) à migration
2) Migration à environment (urban concentrations in
developing countries, etc.)
Basic theoretical
notions about migration: Harris & Todaro: Migration = voluntary action by
individuals; & Zollberg: Migration = forced expulsion
à Harris and Todaro (1970). Migration,
Unemployment and Development: A Two-Sector Analysis.
Full employment flexible
wage model can’t explain Third World urbanization; e.g. Mexico City 20-40 mio.
Migration = voluntary
individual decision, mainly
based on wage differential (rational utility optimisation)
Why do people move to
cities even no there is high unemployment?
RURAL
URBAN
expected utility wage lower expected
utility wage higher because of politically determined wages (signal
quality) significantly higher
Lottery: 1st
price = 100 $. Expected value of a ticket = 1/100 = 1 $.
Subjective
interpretation of expected value; risk avoiding, risk,
Taking, risk-neutral
individuals
U(G) x PG
Critique:
First mover advantage à technology might not be best, but most
widespread
Importance of signals
like wages
à Solution according to H&T: Partial payroll subsidies (marginal
products have to be equal) & measures restricting migration
Discrepancy size resource
– possibilities of adaptation (institutional adaptation) Usually, the adaptive
capability of humans can prevent the eruption of resource conflicts. Human
adaptation has not taken place in instances where there is inequality/asymmetry
of access.
Middle East:
Sometimes it is
difficult to adapt institutions à unsustainability prevails:
Possible adaptation:
technology, property structures, population control.
Historical evidence is
mixed. “Environmental security” is a vague concept, different from the notion
of traditional “security”, which involves a threat and decision making
anticipation. (Schelling: deterring threat; compelling threat). Resource
scarcity rarely acts alone as a source of conflict
Homer-Dixon:
A conflict usually
arises when property rights limit access to a resource. The
decision who has access can be challenged, and enforcement is necessary. So
it’s not the scarcity in and by itself, it’s the mechanism of exclusion that
is a source of conflict.
Olson, The Logic of Collective Action (60’s)
Olson, The Rise and Decline of Nations (80’s): e.g. rise of apartheid in
SA; protectionism of white working class à this sort of mechanism could also be used in
environmental affairs
à Gleick (1993). Water and Conflict.
Access to water = matter
of national security of certain states. Shared rivers, lakes and ground water
aquifers in the Middle East, in India, Rio Grande, …
Water resources as
political and military goals (access)
Water resource systems
as instruments of war (cutting off supply)
Inequitable
distribution: North-South problem; no substitutes; difficult to transport.
Likelihood of conflict
higher in some cases, e.g. sources for irrigation water; joint hydroelectric
dams. (Also: migration, economic destruction)
Climate change:
à More evaporation (Nile –25%)
à Availability of fresh water (rising sea levels)
à Extent to which source is shared
Most water-limited
nations are in Africa and Asia.
Principles of
International Law:
International Law Commission drafted a Law on the Non-Navigational Use of
International Waters: equitable utilization, no harm, information, cooperation,
management of international rivers.
à Luterbacher (1994). International
Cooperation: The Problem of the Commons and the Special Case of the Antarctic
Region.
1959 Antarctica treaty:
preserves the continent for non-military scientific purposes.
Territorial claims not abrogated; new claims prohibited à powerful retaliatory instrument to all parties interested in territory
Why do nations cooperate
without authoritative structures and institutions?
à Axelrod and Olson combined by Luterbacher: perspective that can account
for Axelrod and common good
à Incentive structure exists that induces emergence of cooperative
arrangements even if only (outside and inside) trade offs between coalition are
present
à Antarctica = “common”; underlying threat structure prevents overuse;
powerful can threaten defectors
à Luterbacher and Wiegandt (2000). Water and Property Rights: An Analysis of the
Mid-East Situation.
Linkages between
economic, socio-cultural, political and demographic parts of the social system and
water, which is an important resource sector.
Complexity of social and
climate systems. à Combined physical-social models: Combine
simulation and game theory (differential game)
|
Symmetrical
Access |
Hardin, 1968. |
Privatisation
efficient |
Sequential PD à both can retaliate |
|
Asymmetrical
Access |
Heller and
Eisenberg, 1998 |
Privatisation
inefficient |
Sequential
Chicken à Blockage after first mover acts |
|
|
|
|
|
|
RURAL Climate Change à |
Drought à |
URBAN Demand Water up |
|
|
Climate Change à |
Hydro cycle à |
Supply Water
down |
|
Israel (controls Jordan
river basin), Jordan, Palestine: differential game, sequential PD (retaliation
possible) à solutions easier, e.g. trading through market mechanisms; however, differences
in PR definitions could lead to environmental damage (Coase, Chichilnisky)
Turkey (controls source
of Euphrates), Syria, Iraq upstream-downstream problem: sequential Chicken game
à more difficult to solve
Common pool resource
problems: Competition for first move (better off in the short run). No
possibility to retaliate. Trunctuated chicken game à no cooperation, because retaliation makes second mover worse off than
no retaliation.
à CPR need strong institutions: carrot and/or stick. Example: Montreal
Protocol: developing countries rewarded; non-participants face trade-measures.
à Task for Kyoto protocol: Transferring Chicken into PD game. More
complicated because more than 2 actors, and each actor effectively has veto power.
International trade: If
non-cooperation à retaliation (for a big country) possible
through optimal tariff, at the expense of the rest of the world.
Environnemental
slide shows:
http://www.humboldt.edu/~envecon/ppt/423/
http://www.stoessel.ch/hei/environment/climate_change.htm (Professor Luterbacher)
© 2001 by Marcel Stoessel (marcel (at) stoessel.ch).
All Rights Reserved. This document may only be copied by women, aged 23 to 30,
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