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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
5.2.2. Water Scarcity and Institutional Constraints
The water economy of many countries is entering a mature phase
characterised by inelastic supply of water and increased interdependencies
among water uses and users (Table 5.1.). As the water economy matures,
attention of participants in the policy process is gradually shifting from
concern on the expansion and subsidy of water sector development to
revenue generation, demand management, and reallocation.
In the past, new users could obtain water through appropriating water
rights to which no previous claims had been established. At present, in
countries of Latin America and the Caribbean, although overall supply is
plentiful, in many areas with concentrated economic development, all
surface water, and much of groundwater, is appropriated. New water
supplies have been obtained through the construction of storage and
conveyance facilities, projects usually undertaken with the help of
substantial public subsidies. It is now widely recognized that this policy
has led to investment projects whose real economic viability is doubtful,
and to a wasteful use of water with negative effects on the environment.
Table 5.1. Characteristics of mature water
resource systems.
| Item |
Mature phase |
| Long-run water supply |
Inelastic |
| Demand for delivered water |
High and growing, elastic at
low prices, inelastic at high prices |
| Physical condition of
impoundment and delivery systems |
A substantial proportion is
ageing and in need of repair and renovation |
| Competition for water among
uses |
Increasing |
| Conflicts and externalities |
Rising water tables, land
salinization, saline return flows, groundwater salinization, water
pollution, etc. |
| Social cost of subsidising
increased water use |
High, and rising |
Source: Randall, 1991, adapted by Lee and Jouralev, 1998
Moreover, in many areas, as the best and the least
expensive water sources have been developed and attention increasingly
turns to the more expensive and disadvantageous sources, the costs of new
projects has begun to escalate. Successive increases in reservoir storage
capacity produce diminishing returns in the safe yield. Consequently, as
the options for increasing water supplies through the manipulation of
surface flows diminishes and the subsequent increases in storage require
larger and larger investments, the costs of new projects begin to rise
dramatically. This has been occurring as public subsidies have been
significantly curtailed. It has even disappeared in many countries as a
result of limited public budgets, changing social priorities, lack of
political support for traditional methods of financing water development,
and growing concerns about the environmental costs of new projects.
On the other hand, due to population growth, urbanisation
and economic development, per capita water availability is decreasing.
At the same time that demand for both instream and
withdrawal uses of water expand with economic development and population
growth, water pollution diminishes the available quantities of good water
and increases the costs of treatment. It can be expected that there will
be increasing demands to reallocate supplies among uses.
The driving force underlying the interest in the use of
prices and markets, and on indirect regulatory instruments (i.e., economic
instruments), is the perception that, apart of water being an economic
good, there are substantial gains to be realized. These gains represent
the opportunity cost of failing to modify existing water institutions in
ways that will promote more economically efficient use of available water
supplies. Moreover, there is an additional perception that other
allocation mechanisms will not achieve the desired increases in efficiency
in water use.
It should be highlighted that the institutional fragility
of developing countries and the new emerging economies of the East is now
under higher pressure from lower budget allocation and facing an
increasing demand for environmental regulation. Experiences on the
introduction of economic instruments in this context have been
characterized as initiatives beyond institutional capacity that has
resulted in weak governmental integration and social participation. The
consequent lack of careful analysis and discussion of potential economic
and social impacts arising from these proposals have not allowed consensus
building, which could avoid legal and institutional barriers. Weak social
participation, general public sector crisis and social inequities are very
difficult barriers to overcome and to be framed into sound and enforceable
policies. It is a task to be carried out with great deal of effort and
persistence.
Information building and sharing is key issues to promote
intra- and inter-governmental integration and social participation, which
helps to remove legal and political barriers and merge institutional
strengths. Leadership and expertise of environmental management systems
have to be exercised without insulation. Market-reliance policies are a
favouring factor to market-based initiatives. Therefore it has to be
emphasised and captured in the design of any economic instrument
programme.
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