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Property Rights, Externalities & Environmental problems According to normative criterion, an environmental problem exists when resource allocation is inefficient.

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Presentation on theme: "Property Rights, Externalities & Environmental problems According to normative criterion, an environmental problem exists when resource allocation is inefficient."— Presentation transcript:

1 Property Rights, Externalities & Environmental problems According to normative criterion, an environmental problem exists when resource allocation is inefficient

2 Let’s examine property rights We all, including govt, undervalue environmental assets. capitalist economy: PRs refer to entitlements – use of resource depends on PRs governing them centrally planned economy: people’s needs more important is objective – efficiency Why the interests of individual are different than that of a group? Under what circumstances does this happen?

3 Efficient PR structures 3 main characteristics: I. Exclusivity: C+B to owner II. Transferability: voluntary exchange of rights III. Enforceability: secure from encroachment PRs exchanged in market economy – seller: right to stop consumer from using in absence of payment – consumer: chooses how much to buy at what price for net benefit

4 Consumer’s net benefit Area under AR (dd) curve - cost (expenditure) PS CS D/AR S Q 0 P Price is adjusted by demand & supply, where both maximise their benefits. Efficient allocation by static efficiency. Net benefit= PS+CS VC

5 It is important to find how net benefits are distributed between the consumer & the producer. Efficiency is achieved because of the price system & not because of C/ P’s self interests Adam Smith: selfish people  efficiency Freedom of choice to both Consumers & Producers

6 Scarcity Rent Area under price line is TR Area under MC curve is TVC PS related to profits. It’s = profits + rent new firms enter with rise in price  rent Without price rise - zero rent Most NRs give rise to rent PS in the long run is scarcity rent

7 Externalities A decision maker doesn’t bear cost of consequences of his decision Externality exists when welfare of a firm / an individual depends not only on his activities but also on activities under control of some other agency e. g. waste in river water imposed external cost on resort. Pvt sector doesn’t think of externalities ∴ doesn’t consider cost (control pollutants) for it – produces more quantity at lower price

8 Private MC of steel plant is MCp & for society it is MCs. Price production P*P* Social marginal cost Private marginal cost Q*Q* Qm O Pm With no control on Emission production = OQm – not efficient OQ* is efficient as NB are maximised – if costs external no search for ↓ pollution – releasing waste outside is inefficiently cheap

9 Types of externalities External effects can be +ve or -ve External diseconomy/economy: pollution/garden Pecuniary externalities: when external effect is transmitted through altered prices viz rent ↑ with new entry ∴ all land up paying more rent = -ve effect on all those paying rent. Pollution is not pecuniary externality as the effect is not seen through prices.

10 Improperly designed PRs system Entitlements to resource use: a. Private b. State ownership c. Common property ownership d. Open access regimes: common pool, non -exclusivity & divisibility. Exploited by anyone Capture of resource by one group ↓ availability for others

11 Open-access resources First-come first-serve basis Tragedy of the commons American Bison were plentiful – hunting with no control – aggressiveness of one didn’t affect time & effort by other hunters In absence of scarcity, efficiency was not threatened by open access. As DD  for bison  scarcity ∴ more time & effort

12 Bison harvesting MB slopes downwards as amount of hunting efforts rises, number of bison falls. Thus smaller population supports smaller harvests per unit of effort expended. Excessive exploitation of herd – cannot appropriate scarcity rent ∴ ignore it. Destroying incentive to conserve Harvest effort Total benefits / cost € Total cost Total benefits QO

13 Public Goods Non-exclusivity – non-excludability – landscapes. Air, water & biological diversity Consumption indivisible Biological diversity:  Genetic variability among individuals in single species  Number of species within community of organisms Genetic diversity has proved to be important in development of new crops e.g. disease resistant barley – interdependence of species within ecological communities, a particular species may have more value beyond its intrinsic value

14 Imperfect Market Structure Environment problems – when one of the participants in an exchange of PRs is able to exercise an inordinate amount of power over the outcome – Monopoly – violates definition of efficiency in goods market Monopoly always supplies less and charges more than in competition.

15 Static efficiency is achieved when OB is supplied – net benefit is ∆ HIC. But monopoly will sell OA & charge OF. price quantity MC D/AR A B E MR D C I F G O Producer’s surplus is maximised is clearly inefficient. Society looses net benefit = ∆ EDC H

16 Divergence of Social & Private Discount Rates Producers while achieving max surplus, maximise present value of net benefits under “right” conditions, viz. absence of externalities Firms must use the same rate to discount future net benefits, for efficient use of the resources, that is appropriate for the society Higher rate: extract & sell faster than efficient Lower rate: excessively conservative

17 Private & Social Rates Social discount rate= social opportunity cost of capital Risk premium = additional cost of capital required to compensate owner when actual ≠ expected Risk-free cost of capital – rate of return when no risk = rate expected Therefore, due to the risk premium, the cost of capital is higher in risky business than in no-risk industries. Private & Social discount rates are different as the risk premiums in the two are different.

18 Risk taken by a single person is higher than when it is taken by society as a whole. ∴ private risk > social risk ∴ private discount rate> social discount rate  current production is higher than desirable to maximize net benefits to the society Energy production & forestry both inefficient Private & Social discount rates may not always diverge. If they do, then market decisions are not efficient

19 Government Failure Market & political processes are sources of inefficiency. Improper incentives are the root cause Rent seeking → net benefits to special group → but ↓ net benefits to society as a whole Losers don’t protest? – voter ignorance – economically rational – high cost of keeping informed & low probability that a single voter is decisive – difficult to unite those – opposition to special groups is always under funded

20 Rent seeking – takes many forms - High price under ‘infant industry argument’ - Special subsidies to consumers Govt. policies that are inefficient : rationing, low price of oil, free education to a few…. Policies create evn problems: easy loans for cars → more cars → more pollution Govt. failure - direct challenge: to assumption that intervention by govt. automatically leads to greater efficiency & sustainability.

21 Environmental problems due to divergence between individual & collective objectives – can be resolved by realigning individual incentives to make them compatible with collective objectives Economists reluctant to argue that values of consumers are warped – assume ‘correct set’ of values Capitalism & democracy on presumption: majority knows what it is doing – ballots for representative or $ votes for goods & services

22 The pursuit of efficiency PRs are ill-defined ∴ evn problems To restore efficiency when affected people are a few Example: a Resort & a Steel Plant: o Both are on the bank of a river. o Both have PRs to use river. o Water flowing from plant towards resort. o Resort gets polluted water, due to dumping of waste by the plant. o Its’ clientele is affected.

23 If accepts - returns higher = A+B (surplus)+ C+D (bribe) Price production P Social marginal cost Private marginal cost Q*Q* Qm A B D C O If resort offers a bribe of C+D  less production from OQm to OQ*. Damage less. But if plant refuses  PS = A+B+D. Society better off by C. Net benefits from production OQm = A – C. and from OQ* = A

24 Find: Whom should PRs belong? To the party who seized it first? How to handle environmental risks? Answers By whom? By the court system

25 Resolving the conflict The courts can resolve environmental conflicts by imposing property or liability rules PRs specify initial allocation Entitlement : right to add waste & right to attractive river view Court goes by pre-eminent right –injunction on violating rights injunction removed by the Consent of the party whose right was violated Out-of-court settlement – monetary gain In absence of court - who can seize it easily -naturally Goes to steel co. Court should decide whether to overturn this allocation.

26 Coase Theorem: Ronald Coase (1960) Negotiation costs are negligible + affected parties only a few, court - give PRs to anyone Any way efficient allocation - theorem C-B will change for parties PRs to Co.  bribe by resort PRs to resort  steel co. must bribe = compensation for all damages - ∴ produces OQ* as prv benefits max m. (uses Soc MC as Prv MC due to compensation PRs to resort – cost borne by steel co. PRs to Co. cost borne by resort Either way efficient production

27 Shouldn’t forget administrative cost + lawyer’s fees + court’s time… Govt. can create regulations on pollution control – backed by fines, jail sentence, tax.. Bribes : not the only means If transaction costs high & benefits little – better to live with inefficiency New ways of life: create problems Role of govt.

28 To conclude, producers & consumers determines how the environmental asset is Utilised When PRs system is exclusive, transferable and enforceable, the owner of the resource has powerful incentive to use resources efficiently Economic system will not always sustain efficient allocations


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