McPeak
Lecture 12
PPA 723-F03
Externalities.
An externality occurs when an
economic agent’s consumption or production activities confer a benefit or
impose a cost on other actors, and this benefit is conferred or this cost is
imposed outside of a market.
(that
is to say it takes place in a way other than through changing prices).
Alternatively, an externality
occurs when a person’s well-being or a firm’s production capability is directly
affected by the actions of other consumers or firms rather than indirectly
through changes in prices.
A consumption externality is
an externality generated by the consumption behavior of an economic actor.
Smoke
Drunken louts
Loud music
Passenger vehicle exhaust.
A production externality is
an externality generated by the production activity of a firm.
Smokestacks
Acid rain
Noise and shaking houses
Odors
Externalities can be positive
or negative.
An externality that harms
others by imposing a cost on them is a negative externality.
An externality that helps
others by conferring a benefit to them is a positive externality.
What is a positive
externality to one person can be a negative externality to another (wind
chimes!!).
Positive externalities are
sometimes called spillovers.
Positive externalities play a
prominent role in growth theory and economic development. Also can be used to explain
endogenous neighborhood formation and the persistence of poverty over time in
specific areas.
We are going to focus mostly
on negative externalities here. Private
cost diverges from social cost in the presence of an externality, and in the
presence of a negative externality SC is greater than PC.
Pareto
optimality. An allocation of resources is Pareto optimal
when it is not possible through any feasible changes in the resource allocation
to benefit one person without making at least one other person worse off.
If an allocation is not
Pareto optimal, it is not economically efficient. An allocation is inefficient when it is
possible through some feasible change in the allocation of resources to make at
least one person better off without making any other person worse off.
If an economy does not arrive
at a Pareto optimal outcome, it has suffered from market failure.
In the presence of an
externality, the harmed party is theoretically willing to pay the harming party
to reduce the activity generating the externality, but no market exists for
them to conduct such an exchange.
We may have moral objections
here, but the idea is that I am made worse off by the externality, and there is
some cash value I am willing to pay to eliminate the source of this reduction
in my utility.
Market failure in a
production setting occurs when firms equate private marginal cost with price
rather than social marginal cost with price.
In a competitive market, more
of the good and more of the externality will be produced than is socially
optimal since private cost is less than social cost.
[show graph]
Welfare is maximized when
price equals social marginal cost.
1) A competitive market may produce negative
externalities.
2) The optimal amount of pollution is greater than zero.
Can address
by regulation.
Government can control the
size of the externality by imposing an emission standard that limits the
quantity of the externality imposing byproduct of production.
Can also charge an emissions fee, that taxes the amount of the emission.
If such a tax is designed to
fully internalize the externality, it is called a Pigovian tax.
[show graph]
Taxes on fuels:
|
|
Externality as a % of price |
Tax as % of price |
|
Natural Gas |
1.1 |
6.4 |
|
Gasoline |
16.7 |
16.6 |
|
Diesel |
50.4 |
12.9 |
|
Coal |
528.0 |
35.9 |
Point source pollution is
pollution that can be traced to a single point – there is an identifiable
source of the pollution that can serve as the point of control.
Non-point source pollution is
pollution that cannot be traced to a single point – multiple small sources make
it hard to identify where it originated.
Market
structure and externalities.
Remember that a monopoly
producer selected an output level below the level that would be arrived at in a
competitive market, thus leading to deadweight loss of monopoly.
Remember that a producer that
generates negative externalities is producing more than is socially optimal,
since MSC>MPC.
Can these offset?
Potentially, yes.
[show graphs]
The monopoly output may be
less than the socially optimal level, equal to the socially optimal level, or
greater than the socially optimal level.
It will be less than would be generated in a perfectly competitive
market.
The point is that in the
absence of externalities, social welfare is maximized under perfect
competition. This is not the case if
externalities are present.
Coase Theorem:
In the absence of
transactions costs, and with symmetric information, the initial assignment of
property rights does not matter in determining the efficient allocation of
resources. [though
it may matter from a distributional standpoint]
Cattle
owner and a crop grower.
1)
Is the right to
grow crops without bearing the costs of livestock damage?
2)
Is the right to
graze without facing limits imposed by individuals planting fields?
The rancher is liable to
compensate the farmer for damage in case one, the farmer is liable to
compensate the rancher in case two. From
an efficiency standpoint, the outcome will be the same.
Boat owner rents boats to
cruise about
Chemical firm dumps gunk in
They choose levels of
production, and have the following payoffs.
Initially, assume neither
firm has the right to compensation.
|
Boat Company (boats
used) |
||||
|
|
|
0 |
1 |
2 |
|
Chemical (tons dumped) |
0 |
0 0 |
0 14 |
0 15 |
|
1 |
10 0 |
10 10 |
10 5 |
|
|
2 |
15 0 |
15 2 |
15 -3 |
|
Chemical firm has dominant strategy: BR to anything the boat firm does is 2
Boat firm knows this, chooses 1. 1 boat, 2 tons gunk.
Now assign right to boat firm
that says they must be compensated at $7 per ton
|
Boat Company |
||||
|
|
|
0 |
1 |
2 |
|
Chemical |
0 |
0 0 |
0 14 |
0 15 |
|
1 |
3 7 |
3 17 |
3 12 |
|
|
2 |
1 14 |
1 16 |
1 11 |
|
Chemical firm firm BR is always 1, boat knows this, picks 1 boat. 1 boat 1 ton gunk.
Now assign chemical firm the right to be compensated for any reduction in gunk emission from 2 tons at $6 per ton.
|
Boat Company |
||||
|
|
|
0 |
1 |
2 |
|
Chemical |
0 |
12 -12 |
12 2 |
12 3 |
|
1 |
16 -6 |
16 4 |
16 -1 |
|
|
2 |
15 0 |
15 2 |
15 -3 |
|
Chemical firm firm BR is always 1, boat knows this, picks 1 boat. 1 boat 1 ton gunk.
Why might this break down in
reality?
1) Transactions costs may be high. How to bargain on behalf of one party if they
are many?
2) Lack of information.
What are the costs? Do both sides
know and agree on the MC of the externality?
Is the profit matrix agreed upon?
Tragedy of
the commons.
Where do we have common
property resources?
When a good is rival and has no exclusion.
Rival means one actor’s
consumption of the good in question precludes another actor’s consumption of
the good – the good is depletable.
Exclusion means that others
can be prevented from consuming the good.
The fish in the ocean, the
grass in a pasture, the water in a river, the oil under the ground, a seat in
the lounge, a quick trip down a road, a quick download from the internet…
There is a distinction
between a commons and an open access resource.
In a commons, the number of users is defined, leading to greater
cooperative potential. In an open access
situation, there is no restriction on the number of users.
Commons – the academic
village.
Open access –
Hardin provided the example
of a village commons where multiple users have the right to graze animals. There is an incentive problem in the
commons. Each user has an incentive to
add animals and does not take into account the externality imposed on others
brought about by adding this animal, only the direct costs they bear.
Note the distinction between
an appropriation externality and a provision externality.
An appropriation externality
is a static externality, and it is either your animals or my animals get the
grass to produce milk in this setting.
A provision externality is a
dynamic externality, and it is that together our animals impose a cost on the
future provision of the good produced in the commons, that is we can cause
environmental damage through overgrazing.
There is one pasture we share
in common, and let’s keep it simple and have it be just the two of us using
this.
On this pasture, milk
production as a function of total herd size is as follows:
|
# of animals |
Liters of milk produced |
|
0 |
0 |
|
5 |
10 |
|
10 |
20 |
|
15 |
30 |
|
20 |
36 |
|
25 |
40 |
|
30 |
44 |

For each livestock owner, the
share of this total milk produced they receive is a function of your share of
the total herd. The cash value of milk
is $1 per liter.
For each animal put on the
pasture, it costs $1 in private labor costs.
(5 animals costs $5, 10 animals costs $10,…)
So if I have 5 animals and
you have 5 animals, my payoff is (5/10)*20-5, or 5. If you had 15 animals and I had 5, then it is
(5/20)*36-5, or 4. We can develop the
following matrix of payoffs.
|
|
0 |
5 |
10 |
15 |
|
0 |
0 0 |
0 5 |
0 10 |
0 15 |
|
5 |
5 0 |
5 5 |
5 10 |
4 12 |
|
10 |
10 0 |
10 5 |
8 8 |
6 9 |
|
15 |
15 0 |
12 4 |
9 6 |
7 7 |
(can extend down here to 20 (16,0); 25 (15,0); 30 (14,0))
Can go through and identify
best response strategy. There is a Nash
equilibrium in pure strategies of 15, 15 with a payoff of 7 to each. Note however that if they could restrain
their stocking levels to 10, they would arrive at a Pareto improving outcome.
What if I privatize, and
assign exclusive rights to one of the individuals?
|
|
0 |
|
0 |
0 0 |
|
5 |
5 0 |
|
10 |
10 0 |
|
15 |
15 0 |
|
20 |
16 0 |
|
25 |
15 0 |
|
30 |
14 0 |
I arrive at the efficient
stocking level, as profit is maximized where total herd size for one individual
is equal to 20 and the total payoff is 16.
Not really very fair though,
is it!
What about if we give the
exclusive land right to one of the herders on the condition that the other
herder is allowed to use the land if he pays 80 cents per animal to herder one?
Herder one puts ten animals
on, gets 16 [ (10/20)*36-10+8] while herder two puts
ten animals on and gets zero [ (10/20)*36-10-8]. So this is an alternative that takes you to
the efficient (though not very fair) outcome.
Also consider the possibility
that we develop an outside agency, say the state. This agency is able to impose a herd size
limit of 10 animals per person and is capable of enforcing this.
Finally, consider the state
charging a user fee of 50 cents per animal in addition to the one dollar per
animal labor cost. The
following payoff matrix results.
|
|
0 |
5 |
10 |
15 |
|
0 |
0 0 |
0 2.5 |
0 10 |
0 15 |
|
5 |
2.5 0 |
2.5 2.5 |
2.5 5 |
1.5 4.5 |
|
10 |
5 0 |
5 2.5 |
3 3 |
1 1.5 |
|
15 |
7.5 0 |
4.5 1.5 |
1.5 1 |
-0.5 -0.5 |
This also takes us to the
socially efficient stocking level of 10, 10. Now the state gets 10 in tax revenue as well.
[localized
degradation paper]
Responses to the commons:
1)
Land tenure
reform (assign rights – think Coase)
2)
Limit use
(restrict quantity – think emissions standard)
3)
Charge fee that
internalizes the negative externality (think emissions fee).