Estimating Irrigation Subsidies: The Need for a Common Methodology
By Ravinder P.S. Malik
Agriculture is the leading consumptive user of water, accounting for between 70 to 90 percent of the total water used in developing countries and more than one third of the water consumed in many OECD countries.
In most countries, water for irrigated agriculture
is subsidised by governments, with far reaching
implications for food security, patterns of agricultural
development, trade, government finances, and,
more generally, the sustainable use of water.
Some of the available evidence, such as from
India, shows that subsidies for irrigation have
promoted inefficient use of water, contributing
to steep declines in levels of ground water. Indeed,
at a time when water scarcity is a looming crisis
in many countries, the need to reform subsidy
regimes for irrigation is urgent.
As a first step, reforming irrigation subsidies
requires a clear understanding of the concept
of a ‘subsidy’ and the methods that
are used to estimate that government support.
Generally, subsidies to irrigation water are defined
and measured from two different perspectives:
from that of the water-supplying agency (generally
a government or government agency) and from the
beneficiary (user) of the irrigation water. Of
the two approaches, the first approach has been
used more widely to define and measure subsidies.
Under this first approach, subsidies are usually
calculated as the difference between the cost
of supplying irrigation water and the revenue
realised from its sale. However, both the key
elements on which the estimation of subsidy is
based — ‘cost’ and ‘revenue’
— have been measured and interpreted differently
depending on the analyst. Several characteristics
of irrigation works have contributed to these
variations. Most are multipurpose: in addition
to providing water for irrigation, they may also
supply water for municipalities, industry, hydropower,
navigation, tourism and fisheries, as well as
providing flood protection.
Moreover, while most of the large projects are
built and maintained by governments or their agencies,
small groundwater-based systems are often owned,
operated and maintained by individual farmers,
in some cases with governments providing support
via low electricity tariffs for pumping.
Estimating the cost of providing irrigation water
is further complicated by a host of other factors
that need to be addressed. These include: how
to apportion the capital costs of irrigation in
a multipurpose project? Should capital costs be
treated as sunk cost? What assumption should be
taken as the life of the project? Should the cost
of externalities be accounted for? If so, how
should the cost of environmental degradation be
quantified? Are the necessary data available to
estimate these costs?
There are similar issues that need to be resolved
on the revenue side. Are farmers the only beneficiaries
of irrigation water? Do other sections of the
society also gain from the availability of irrigation
water? Are there any other revenues in addition
to the irrigation charges to the government from
the sale of irrigation water? Is enough data available
to estimate revenues?
As it is, an assortment of methods has been used
to estimate costs and revenues. And because the
methodologies are different, the estimates are
usually not comparable. For example, when estimating
costs, some analysts consider only the operation
and management costs; others add some fraction
of capital cost, but without clarifying how the
cost of multipurpose projects have been apportioned
and how the capital invested in the past has been
accounted for. If irrigation subsidies are to
be measured in a way that make their estimates
more meaningful, comparable and useful, a consensus
on a working and widely acceptable definition
of irrigation subsidies and their methods of measurement
is vital.
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