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Newsletter and Technical Publications
<Planning and Management of Lakes and
Reservoirs: An Integrated Approach to Eutrophication>
CHAPTER 5: ECONOMIC ASPECTS OF EUTROPHICATION
5.2. Allocation of Water Resources and Eutrophication
5.2.3. The Economics of Eutrophication
As eutrophication increases, the productive potential for water, under
some circumstances, diminishes; the value (potential) of a unit of water
cannot be realised. Eutrophication created by an individual can generate
costs to other users of the water resource, both consumptive (drinking
water) and non-consumptive productive uses (agriculture).
At one extreme, water users may choose water practices, which degrade
the productive potential of the resource, increasing eutrophication and
causing a reduction in the productive or amenity value of water for other
users. This scenario may produce relatively high income, through cost
savings, in the short run, but leads to reduced utility from water for
others. At the other extreme, water users may reduce - and possibly
eliminate - eutrophication thereby reducing income in the short run, due
to excessive costs of control, but improve the income for others. There
are many points between theses two extremes. The economic impact of
eutrophication can be shown in a partial equilibrium framework as
discussed later in this chapter.
There is also a temporal element associated with eutrophication.
Siltation is not apparent in the short run, however, the long run economic
returns from water storage can be reduced. Eutrophication is a complex
problem because of the space and time aspect of each management decision
(i.e., impact). The economic instruments and policies discussed here focus
on a static analysis of the economic impacts. This does not exclude the
temporal effects but assumes that market mechanisms will internalise the
long run effects.
Eutrophication is most commonly perceived as being a negative
externality. The impact of eutrophication may produce positive benefits to
some wildlife species but increase the incidence of the algal blooms
resulting in costs. It could be argued that an increase in the nutrient
levels of water might be of benefit to an irrigator, however this section
will focus on negative impacts.
Finally, since a significant portion of anthropogenic eutrophication is
a by product of land use then the economics of changes in land use and
land use practices must always be considered in the context of the
management and control of eutrophication.
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