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ECON 4910 Spring 2007 Environmental Economics Lecture 6, Chapter 9
Lecturer: Finn R. Førsund Environmental Economics
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Illustration of spatial dimension
Spatial configuration: transport from source to receptor Key variable: transfer coefficient aij i Transfer coefficient Source i (Point, Mobile, Diffuse) akij Spatial dimension of environmental problems of interest, will influence the optimal solution One solution to a local pollution problem may be to move either the source or the victims Transport from source to environmental receptor of interest, air, water, dilution, retention, deposition on the way Environmental receptor, j Environmental Economics
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Spatial dispersion of pollutants
Non-uniform dispersion ei = vector of secondary or remaining discharges of pollutants from source i eki = discharge of pollutant of type k from source i Msj = environmental service of type s measured by indicator at receptor j Environmental Economics
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Non-uniform dispersion of pollutants
Introducing transfer coefficients The unit transfer coefficient akij is a pure reorganisation of the environmental function summing up the amount of a pollutant reaching the environmental receptor Environmental Economics
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Non-uniform dispersion of pollutants, cont.
Marginal impact on environmental services is depending on the location of the source i The transfer coefficient may also depend on level of emission of other substances if physical interactions Special case of constant transfer coefficient Must also consider the time dimension Environmental Economics
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One-directional diffusion of pollutant
Pollution of a river, simplifying to one pollutant and fixed transfer coefficients Ordering the sources along the river starting upstream of receptor j The transfer coefficient of source most upstream must be the smallest due to retention Define retention: falling to the bottom, eaten up, worked on by bacteria, aquatic life, sedimentation Environmental Economics
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Illustration of river pollution
Downstream Source i Receptor j Define retention: falling to the bottom, eaten up, worked on by bacteria, aquatic life, sedimentation Environmental Economics
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One-directional diffusion of single pollutant, cont.
Marginal impact from source i to the same receptor j gets successively larger for sources downstream Dissolved oxygen and organic waste Environmental Economics
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The social solution, non-uniform dispersion
The social optimisation problem adopting monetary evaluation of environmental services Assuming the monetary evaluation of the same service level is independent of receptor First-order condition Marginal purification cost equal to marginal evaluation of the environment Environmental Economics
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Implementation using a Pigou tax
Firms minimise costs plus tax payment First-order condition Comparing the social solution and the market solution yields the optimal tax Tax rate function of the dispersion of the pollutant and the impact on environmental services Environmental Economics
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The case of polluting a river
Must look at pollution caused by source i: Ri is the set of receptors polluted by source i Load in receptor j is also coming from all upstream sources, but by assuming additivity of load these effects can be neglected Environmental Economics
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Environmental Economics
River pollution, cont. The first-order condition in the social solution Simplifying to the same biological effect and monetary evaluation of the environmental sevice Environmental Economics
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Implementing using a Pigou tax
Finding the optimal tax rate The tax rate becomes smaller the further downstream the location of the source Environmental Economics
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Uniform dispersion of pollutants
Uniform dispersion implies that all transfer coefficients are equal and typically equal to 1 Environmental Economics
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Uniform dispersion of pollutants, cont.
Marginal effects The marginal effect is independent of source, i.e. location, but depends on type of pollutant Environmental Economics
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The social solution, uniform dispersion
The social optimisation problem (simplifying to one pollutant and one environmental service) First-order condition Marginal purification cost equal to total marginal evaluation of change in environmental service Environmental Economics
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Implementing the social solution using a Pigou tax
Finding the optimal tax rate The tax rate is independent of source implying the same marginal purification cost for all sources and equal to the total marginal monetary evaluation of the environmental service Environmental Economics
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Tradable emission permits
Trade in permits can be used when the social solution is derived from setting environmental standards because the damage function is not known Damage function known, but certainty of achieving the desired pollution level is preferred Trade in permits to a common trading price can only be socially optimal if the pollutant is uniformly dispersed Environmental Economics
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Tradable emission permits, cont.
Modelling one receptor, one pollutant , multiple sources Policy problem: how to distribute emission permits on the sources in order to achieve the environmental standard to least cost Policy options Auction the permits Giving them free, following e.g. a grandfathering principle Environmental Economics
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Tradable emission permits, cont.
Finding the restriction on total emission If the dose-response functions are known, goals for environmental services, , will determine the total emission restriction Environmental Economics
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Tradable emission permits, cont.
How to set the firm-specific quotas Grandfathering: uniform reduction Least cost allocation Environmental Economics
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Least cost allocation, cont.
The Lagrangian First-order condition Environmental Economics
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Least cost allocation, cont.
The least cost solution: Marginal purifications costs should be equal for all firms Comparison with uniform reduction solution Environmental Economics
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Market implementation of emission permits
Giving quotas free, allowing free trade A firm can keep a permit or sell it to other firms Assume a market with a price for quotas Analogy with the Coase theorem Assume an auction ending with a competitive price q: min sum of purification cost and outlay on quotas, same solution as above Environmental Economics
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