The
world currently produces enough food to feed itself and is expected
to continue doing so until 2050 when populations are predicted to
stabilize at around 10 billion. Still, meeting predicted global food
security needs will require considerable effort to increase food
output. At the same time, there will be additional demands to solve
hunger problems brought about by distribution and access
deficiencies in particular regions and for particular groups of
people in those regions, even in the midst of global food abundance.
A large part of the solution to global and regional food problems is
likely to be found through irrigated agriculture.
However, the World’s
population has doubled from 3 billion in 1960 to 6 billion in 2000.
The nutritional demands have also risen from 2,255 kilocalories per
person per day (kcal/cap/day) in 1961 to around 2,800 kcal/cap/day
in 1998 (Webb, 2002, 2001). Yet the cropland area increase has been
only modest from 1.36 billion hectares in 1960 to 1.47 billion hectares in
1990 (see Ramnakutty, and Foley, 1999, 1998). Based on various
estimates, it has remained around 1.5-1.8 billion hectares at the
end of the millennium (World Resources
1992-1999, Ramanakutty and Foley, 1988),
of which about 16-18 percent is irrigated (FAO, 2001). Irrigated
areas are also increasing at much slower phase of about 1.3 percent
per year at present when compared to 2.6 to 3 percent during the
peak irrigation era of 1960-1980 (e.g., see in Postel, 1999). Given
these facts, how does the World feed itself?. It is widely accepted
that cultivation intensities (more than one crop a year especially
through irrigation) and increased gain yields have been meeting the
World’s food demand in recent decades. But what is the extent of the
increase in cultivation intensities in irrigated lands?. There are
no estimates of this. What are the spatial distributions of these
irrigated areas in the World?. Further, with overwhelming proportion
of all the water use is for irrigation, an accurate estimate of
intensities of irrigated lands will be crucial to determine
consumptive use of water by crops, and cropland dynamics over space
and time. The need to set a platform for consistent future estimates
of irrigated areas and related information can not be overemphasized
in a World that will need to feed ballooning population in a scarce
Land and water resources.
Irrigation is widely
thought to provide 40% of the world’s food from around 17% of the
cultivated area, and has been an instrumental factor in the success
of the ‘Green Revolution’ in meeting food needs over the past 40
years, particularly for staple grains. These successes have come at
significant environmental costs through river regulation and land
and water degradation from inputs to intensive agriculture. For
example, irrigation typically consumes over 70% of diverted water
resources in Asia, where irrigation
development has been mainly concentrated. Key questions concerning
the sector include:
o
How much irrigation do
we have now?
o
How much do we need in
the future?
o
How much do we want in
the future to achieve a sustainable balance with the
environment?
o
How
much water does it require and will this be
available?
Previous efforts to
quantify the amount of irrigation in the world have relied on
secondary statistics, which in many instances systematically over or
under-estimate actual cropped irrigated area. For example, some 60%
of irrigation in
India
now is practiced using groundwater, most of which is privately
developed and not necessarily recorded in government statistics.
Irrigated areas of the World in the past have been accounted
primarily using the Government statistics and place global equipped
area for irrigation between 250-280 million Ha. These estimates use
a combination of statistics, existing GIS and other techniques to
indicate the distribution of irrigated areas in different parts of
the world. The best known of these is the Food and Agricultural
Organization of the United Nations and the University of Frankfurt
(FAO\UF) derived global map of irrigated areas (Siebert et al.,
2006, and Siebert et al., 2005).
While these being
excellent efforts, there is still substantial room for improvement
in estimates, and this is the impetus for the IWMI global irrigated
area map (GIAM). The IWMI
GIAM is derived from a great variety of remote sensed data at
different geographical and time scales, in the expectation that the
vegetation dynamics revealed will:
1)
define more precisely
the actual area and precise spatial distribution of irrigation,
and
2)
elaborate the extent of
multiple cropping over a year, particularly in
Asia, where two or three
crops may be planted in one year. This is especially useful since
cropping intensities are not accurately known or recorded in
secondary statistics.
The major finding of
the IWMI GIAM analysis is the
reporting of irrigated areas with and without intensity.
The annualized
irrigated areas (AIA) considers intensity of irrigation and is
equivalent of gross cropped area under irrigation. The AIA was
determined to be 467 million ha. This very significantly exceeds the
estimates of equipped area of FAO\UF at 274 Mha (Siebert et al.
2006, Siebert et al. 2005) and others (257 to 280 million ha)
(van Schilfgaarde, 1994,
Siebert, S., Döll, P.,
Hoogeveen, J., 2002), due to the extent of
multiple cropping and private and community developed irrigation.
The area estimates in the map are derived for each characteristic
agricultural systems around the world (e.g. long season winter sown
cereals in the northern hemisphere; triple rice cropping in SE Asia;
wet monsoon season (Kharif) and dry winter (rabi) systems in the
Indian sub-continent). We have summarized the
statistics for three notional cropping seasons running from
June-September (including single long season crops harvested in this
period), October to February, and from March to
May.
The estimated areas are
252,
174
and
41
million
Hectares,
respectively.
The total area
available for irrigation (TAAI) does not consider intensity of
irrigation and is equivalent of net irrigated areas (NIA) which is
determined to be 399 Mha. The figure of 257 million Hectares equates
to equipped area in FAO and other estimates (257 Mha to 280 Mha),
and the development of global irrigated area is summarized in the
chart, with and without estimates of cropping
intensity.

Historical development of global irrigated area, with and without cropping
intensity expressed in Million
Hectares.
It
is useful to present the gross irrigated area according to seasonal
breakdown that reflects cropping intensity as presented in this
study (see next paragraph and the documentation for details).
However, at global level, further refinement maybe necessary in
order to account for varying seasonality by taking more precise
cropping calendars between northern and southern hemispheres, the
tropics, and the higher latitudes.
The
IWMI Global Map of
Irrigated Area (GMIA) map and related products is published on a
website that includes full documentation of the results and the
techniques used:
http://www.iwmigiam.org
The map has a nominal
resolution of 10 km2 per pixel, as monthly
time series NOAA AVHRR (1997-1999) images provide the core data. The
SPOT Vegetation monthly 1-km data of 1999 was also used in
identifying and delineating classes, with irrigation within the
forest cover in Africa and
South
America identified using 100m
resolution JERS-1 radar imagery. The 30-150 meter
hi-resolution Landsat derived imagery (GeoCover) was used to refine
irrigated and land-use classes. Extensive use has been made of
groundtruth data from a wide range of sources, including extensive
IWMI work in the Ganges and
Krishna basins in India, by AIT team in Thailand, the innovative
Degree Confluence Project data that samples the World at every 1
degree by 1 degree based on volunteer contributions, and the IWMI’s
ground truth data of the World (http://www.iwmidsp.org).
Masks of rainfall, elevation, temperature, and forest cover have
also been used to define and refine the classification.
The GIAM provides 28
unique irrigated area classes of the World, with 10 surface water
classes and 18 groundwater\conjunctive use classes. The
characteristic spectral and time-series signatures are attached for
each of the 28 classes. These characteristics indicate whether the
area is single, double or continuously cropped. The estimated areas of
irrigation per pixel were extracted using a new technique called
sub-pixel de-composition technique, which is described in the
documentation and “area story” of the website. It must be noted that
there is a more disaggregated irrigated area map with 343 classes.
Such a map maybe useful for users specifically interested in greater
details, specifically when one is focused on a particular country or
continent. But the users will have to further refine class names
based on local knowledge.
The website
additionally contains three other global agriculture products and
their associated documentation:
·
Global map of Rainfed
Cropped Areas
(GMRCA)
·
Global map of all land use/land cover (LULC) areas
(GMLULCA)
·
Global IWMI generic
951 class map
(Generic-IWMI-951)
Work on irrigated area
mapping continues @ IWMI with: 1) refinement and upgrading the
global map using high resolution images and other refinements, and
2) the development of a much more detailed 500-m pixel scale map of
the entire Indian sub-continent, consisting of 7 Countries.
The extent of estimated
gross irrigated area has some significant ramifications for current
understanding of irrigation and its contribution to global food
security, especially in relation to total global cropped area,
estimated at 1.539 billion ha in year 1999 (also at
http://www.iwmigiam.org.
The team seeks feedback
from all users, readers and interested parties, and continues to
harvest groundtruth data to verify and upgrade the map. We welcome
your views and contributions,
please!!
References
FAO, 1998. FAOSTAT,
Internet version (http://www.fao.org). Food and Agricultural
Organization of the United Nations,
Rome.
Food and Agriculture
Organization. 2001. FAOSTAT database. Available
http://apps.fao.org. Cited
February 9,
2001.
Framji, K.K., Garg
B.C., and Luthra, S.D.L. 1981. Irrigation and drainage in the world
:a global review. Third Edition, ICID,
New
Delhi.
Ramankutty, N., and J.
A. Foley. 2003. LBA Regional Historical Croplands, 5-min, 1900-1992
(Ramankutty and Foley). Data set. Available on-line
[http://www.daac.ornl.gov] from
Oak
Ridge
National
Laboratory
Distributed
Active
Archive
Center,
Oak
Ridge,
Tennessee,
U.S.A.
Ramankutty, N. and Foley, J.A. 1999. Estimating
historical changes in global land cover: Croplands from 1700 to
1992. Global Biogeochemical Cycles 13,
997-1027.
Ramnakutty, N., and J.
Foley, 1998. Characterizing patterns of global land use: An analysis
of global croplands data. Global Biogeochemical
Cycles, 12(4):667-685.
Postel, S., 1999.
Pillar of Sand: Can the
Irrigation Miracle Last?
(New
York:
W.W. Norton). Pp. 313.
Siebert, S., Hoogeveen,
J. & Frenken, K. (2006): Irrigation in
Africa,
Europe
and LatinAmerica - Update of the
Digital Global Map of Irrigation Areas to Version 4.
FrankfurtHydrology Paper
05,
Institute of
Physical
Geography,
University of
Frankfurt,
Frankfurt am
Main,
Germany and Food and
Agriculture Organization of the United Nations,
Rome,
Italy.
Siebert, S., Döll, P.,
Hoogeveen, J., Faurès, J-M., Frenken, K. & Feick,
S.
2005.
Development and
validation of the global map of irrigation
areas. Hydrology and Earth
System Sciences, 9, 535-547.
Siebert, S., Döll, P.,
Hoogeveen, J., 2002. Global map of irrigated areas version 2.1.
Center for Environmental Systems Research,
University of
Kassel,
Germany, and FAO,
Rome,
Italy.
Online documentation and download
of 5 min map of irrigated area version
Thenkabail, P.S.,
Biradar, C.M., Turral, H., and Schull, M. 2005. A Global Map of
Irrigated Area at the End of the last Millennium using Multi-sensor,
Time-series Satellite Sensor Data. Draft Documentation for:
http://www.iwmigmia.org. International Water
Management Institute (IWMI),
Colombo,
Sri
Lanka.
van Schilfgaarde, Jan,
1994. Irrigation- a Blessing or a Curse.
Agricultural Water
Management
25: 203-219.
Webb P., 2001. Land
Degradation in Developing Countries: What is the Problem?.
International Journal
of Agricultural Resources, Governance and Ecology
1
(2): 124-36Wiebe
Webb, P. 2002. Cultivated Capital:
Agriculture, Food Systems and Sustainable Development,
Food Policy and Applied
Nutrition Program. Tufts Nutrition. DISCUSSION PAPER NO.
15. The Gerald J. and
Dorothy
R.
Friedman
School of Nutrition Science
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** = These seasons
correspond directly to Kharif (June-September), Rabi
(October-February) and Summer (March-May) in the Indian
sub-continent, which is one of the major irrigated regions of the
world. One can easily refine these cropping calendars more precisely
taking different regions with unique crop calendars. However, the
cropping seasons in different parts of the World fall within one or
the other above crop calendars. For example, the main and the only
cropping season of mid-western
United States of
America is during
May/June-September/October that is well captured using Kharif
seasonality. The main cropping calendar in Near
East (e.g.,
Syria) goes from November
though May with little or no growth of early germinating crops
during winter (November-February) months when crops hibernate due to
low temperatures and begin swift growth and maturing during
March-May when temperatures are conducive. These areas are captured
during the above Summer (March-May) calendar.