Natural Resources and The Environment
Customary supply and demand graphs show how rapidly a good is being
consumed. For exhaustible natural resources, conservation takes
place when the quantity on the horizontal axis moves to the
left. Conservation can be achieved by shifting the supply curve
on such a graph to the left.
The cost of extracting a resource is one of the forces affecting the
location of the supply curve. Easily accessible deposits, with
low extraction costs, are generally used first. So, other things
being unchanged, as more and more of the resource is used, the
supply curve for an exhaustible resource
tends to shift to the left and encourages conservation.
As exhaustible natural resource prices rise, it pays firms and
individuals to search more vigorously for new deposits of the
resource. For this reason, "proven reserves " often
increase as prices rise.
The conservation effect of shifting the sup ply curve to the left is greater when the price elasticity of
demand for the resource is high, and it is smaller when price
elasticity is low. Since price elasticity of demand is usually
greater as the length of
time increases, conservation effects of supply curve shifts
increase with the passage of time.
Low interest rates encourage the conservation of exhaustible natural
resources, and high interest rates discourage conservation,
other things being equal. This is so because high interest rates
mean, for resource owners, that alternative uses of their wealth
are more attractive than leaving that wealth in its natural
state as a resource.
Because interest rates reflect time preferences and the productivity of
capital goods, they provide a connection between resource
conservation and other aspects of an economic system.
Conservation of exhaustible natural resources is just one aspect
of the many different choices between the present and the
future.
Interest rates may fail to provide appropriate guidelines for
conservation. Central bank policies, government budget surpluses
or deficits, and tax policies relating to saving and investing
all can influence the real interest rate in the economy.
Monopoly power exists in some natural resource markets. Since
monopolistic firms tend to restrict output in order to increase
profits, they may help to conserve exhaustible natural
resources. However, much depends on the specific circumstances
and policies followed by these monopolistic enterprises.
Government tax policies and price controls can affect the conservation of
exhaustible natural resources. U.S. preferential tax treatment
for natural resource extraction may have speeded up the use of
some resources. However, price controls on natural gas and on
oil may have slowed down the use of these resources.
For renewable resources, conservation calls for attention to the economic
factors that determine the conditions for the reproduction and
growth of such resources. Because property rights are not
clearly defined in some areas, human activities may have reduced
renewable resource habitats too much and worked against the
conservation of these resources.
Conservation of renewable resources also may require some limitations on
the annual harvesting of these resources. The sustainable -
annual yield curve shows the quantities that may be harvested
without causing a change in the population of the species. To
conserve the species, harvesting should not be allowed to exceed
the sustainable yield.
The common property system sometimes fails to ensure that harvesting of
renewable resources does not exceed the sustainable yield.
Government regulations may be used to limit harvesting in common
property areas. Extending the scope of private property rights
is another way the control harvesting. The concept of a
reservation price shows how property rights build future
interests into present decisions about resource use.
The laws of the conservation of energy and matter suggest that waste
treatment cannot reduce the total amount of waste but can change
the forms and locations of waste dispositions.
The demand for nature's waste-disposal services is derived from the
demand for the goods and services that produce the waste. Waste
disposal generates social costs through its disruption of
natural ecological systems. In economic terms, the efficient
quantity of nature's waste-disposal service is achieved when the
value of the marginal unit of waste-disposal service, as
indicated by the demand curve, is equal to the social cost of
that unit.
Waste-disposal charges (effluent charges) can make up for nature's
inability to charge a price as a condition for disposing of
waste. Correct effluent charges can establish a supply curve and
bring about the efficient quantity of waste-disposal service.
Externality problems arise in waste disposal because property rights are
not well established or enforced for waste disposal into public
areas. Government can improve the efficiency of waste disposal
by exercising property rights in areas where private property
rights are not established.
Effluent charges lead to price rises to producers and consumers for goods
and services that generate harmful externalities. In this way
they provide incentives for consumers' to switch to other goods
and services and for producers to find methods of production
that cause less waste. These are attractive features of effluent
charges. Developing reliable estimates of the actual demand and
costs of waste is the main problem with these charges.
Standards and controls are a means of limiting waste by specifying
product characteristics and methods of production and waste
treatment. These methods of controlling the volume of waste are
attractive politically. However, economists are critical of
standards and controls because they tend to lock production and
treatment methods into current technologies and to offer little
incentive for developing better technologies.
Subsidies for waste treatment are criticized by economists because they
tend to lower costs to producers and prices to consumers of
goods that generate waste and in this way tend to increase the
total volume of waste.