Overview
On the sidelines of the Global Irrigated Area Mapping (GIAM) International Workshop, an interested group met to discuss the possibilities of bringing out a peer-reviewed publication on Global irrigated area mapping. After much discussions, majority agreed to:
“Bring out a book on irrigated areas
that will be, preferably, preceded by an e-book”
To move forward in this, the following points have been
identified.
I. Title
Global Irrigated Areas
An Assessment from Spaceborne
sensors, other Geospatial techniques, and from National Statistics
Editors: Prasad S. Thenkabail, Hugh
Turral, and Chandrashekhar M. Biradar
II. Chapter outline
| Foreword |
Tom
Loveland et al. |
1.0 Introduction
Chapter 1.1
Introduction to Global irrigated areas |
Hugh
Turral et al. |
Chapter 1.2
A brief history of irrigated areas of the World |
Prasad S. Thenkabail et al. |
|
|
2.0 Global irrigated area mapping
methods and results
Chapter 2.1
IWMI’s Global irrigated area map (GIAM) from remote sensing |
Prasad Thenkabail et al |
Chapter 2.2
Global map of irrigation areas 4.0 (GMIA 4.0) - mapping
irrigated areas
by combining sub-national statistics and geo-spatial data.
|
Stefan Siebert et al. |
| |
|
3.0 Continental and National
Irrigated Area Mapping methods and results
Chapter 3.1
Mapping irrigated agriculture over the Continental US
using multi-temporal MODIS data |
Mutlu
Ozdogan et al. |
Chapter 3.2
Estimating
spatio-temporal patterns of continuous
Paddy field cover using MODIS time series |
Wataru
Takeuchi et al. |
Chapter 3.3
Assessment of availabilities and demands of water resources
in river basins |
Roland Geerken et
al. |
Chapter 3.4
Mapping paddy rice of Asia using MODIS time-series |
Xiangming
Xiao et al. |
Chapter 3.5
Semi-supervised technique to retrieve irrigated crops from
Landsat ETM+
imagery for small fields and mixed cropping systems of South Asia |
Nilantha Gamage et al. |
Chapter 3.6
Irrigated Area Mapping for China - Challenge and Feasibility |
Songcai
YOU et al. |
Chapter 3.7
Irrigated Areas of India through Synergy between
Satellite Sensors data and National Statistics |
Obi
Reddy
Gangalakunta
et al |
Chapter 3.8
Satellite remote sensing and GIS based irrigated area
mapping in
Godavari river basin of India
|
Jayashree Pachpute
et al |
Chapter 3.9
Irrigated area in India over the last 50 years: Past
expansion and present trends |
A.
Narayanamoorthy et al. |
Chapter 3.10
Irrigated areas of Pakistan over last fifty years |
Rakshan
Roohi et al. |
Chapter 3.11
Mapping irrigated areas of Iran using remote sensing data |
Abdolreza
Ansari Amoli et al. |
Chapter 3.12
Multi-angle spectral measurements for classifying cropping areas |
Francis
Canicius et al. |
Chapter 3.13
Mapping the irrigation area for the estimation of agricultural water demand in
North China plain MODIS remote sensing data |
Zhihai Qin et al. |
Chapter 3.14
Ground water abstractions estimates based on satellite images and ground truth
An example from water scarce region of West Asia. |
Schweers Wilko et al. |
| |
|
4.0 Mapping conjunctive use and
groundwater irrigated areas
Chapter 4.1
Conjunctive Water use Area Dynamics and its Mapping using
Multi-temporal IRS Data |
Praveen
Gupta et al |
Chapter 4.2
Groundwater irrigation mapping in the Ogallala Aquifer, USA |
Bethany Bolles et al. |
| |
| 5.0 Comparing irrigated areas from
National statistics and remote sensing approaches |
Chapter 5.1
Irrigated Areas of India based on Satellite Sensors and
National Statistics: Issues and |
Obi Reddy |
Chapter 5.2
Way forward from Global Irrigated Area Mapping (GIAM)-2006 |
Gangalakunta
et al |
| |
|
6.0 Mapping irrigation
potential
Chapter 6.0
Irrigation potential creation and realization |
Venkateswara
Rao et al. |
| |
|
7.0 Applications of irrigated area
maps
Chapter 7.1
Mapping the spatial distribution of irrigated areas and volumetric
water demand in a temperate climate: a case study in England and Wales |
J.W. Knox et al |
Chapter 7.2
Using MODIS Thermal Data for
Estimating Actual Evapotranspiration from Irrigated Fields |
Senay,
G.B et al |
| |
|
8.0 Global Rainfed croplands
Chapter 8.1
Global map of rainfed croplands and comparisons with
irrigated areas |
Chandrashekhar M.
Biradar et al. |
| |
|
9.0 Accuracy and error assessments
of the global maps
Chapter 9.1
Accuracy assessment |
Russ
Congalton et al. |
| |
|
10.0 Lessons learnt and the Way
forward
Chapter 10.1
What was achieved and where we want to go? |
Prasad S. Thenkabail et al. |
| |
|
III. Peer
review panel
Prasad S. Thenkabail (coordinator)
Hugh Turral
Mutulu
Ozdogan
Eddy
De-Pauw
Jerry Knox
IV.
Manuscript submission
The book chapters
will be peer-reviewed before publication. Manuscripts will be coordinated by Prasad S. Thenkabail (p.thenkabail@cgiar.org).
Please submit the manuscripts directly to Prasad (either as e-mail attachment
or ftp upload\download). Please contact Prasad / Chandru if you need ftp upload
location. You can also set up a ftp location and send an e-mail to Prasad to have it downloaded.
Prasad will coordinate with the
peer-review panel members (see section III) to have the papers reviewed. Every
peer review member will handle few papers and have them peer-reviewed by at
least 2 independent reviewers.
V. Page
limits and formats
The full
length articles must follow the following minimum standard:
A. Length:
less than 50 pages including figures and tables
B. Font:
times new roman 12”
C. spacing:
double, single sided
D. Front
page: with title, key words, and contact details of the author\s including
e-mail
E. Figures:
high resolution tiff. Up to 5 color images allowed (this will depend on
agreement with publisher and may change).
F. Text,
figures, and tables: for review insert tables and figures at appropriate
portion of the text.
VI. Time
line for manuscript submission, review, and publication
October 30, 2006
November 30, 2006
January 31, 2007
May 31, 2007
August 31, 2007
October 31, 2007
December 31, 2007
January 31, 2008
June 30, 2008
October 31, 2008
|
Final list of authors and chapters ready for discussions;
Final list of authors and chapters decided;
Discuss and decide on the publisher
Manuscript submission
First review over
Manuscript re-submission with peer-review comments addressed
Second review over and finalization of selected papers
Book goes to press
Proof from press
Book released |
| |
|
VII. Process
We will try and be flexible in the contributions. For
example, we welcome manuscripts on topics not listed above such as innovative
methods (e.g., scale, area calculations) in mapping irrigated areas or
irrigated areas of other Countries (not in the list above). However, the peer
review process and the relevancy of the contribution is a must and will be strictly
adhered to in the selection process. Obviously, all contributions can not be
accepted and some may have to be rejected (based on peer review and relevancy).
This need to be kept in mind by the contributors.
VII. Accepted article instructions
Detailed instructions will be sent to authors of accepted
articles for preparation of the final manuscript.
Appendix I – Email List
loveland@usgs.gov
h.turral@cgiar.org
p.thenkabail@cgiar.org
s.siebert@em.uni-frankfurt.de
ozdogan@hsb.gsfc.nasa.gov
wataru@iis.u-tokyo.ac.jp
roland.geerken@yale.edu
xiangming.xiao@unh.edu
a.mobin@cgiar.org
yousc@igsnrr.ac.cn
obireddy@nbsslup.ernet.in
na_narayana@hotmail.com
drroohi@hotmail.com
aansari@isa.ir
pkgupta@sac.isro.gov.in
seelan@aero.und.edu
bkurz@undeerc.org
vvrao@nrsa.gov.in
j.knox@cranfield.ac.uk
senay@usgs.gov
c.biradar@cgiar.org
russ.congalton@unh.edu
jaishree_kumkar@rediffmail.com
franciscanicius@yahoo.com
w_schweers@caas.ac.cn
qinzh@caas.net.cn
Appendix II - Submitted abstracts
A Global
Irrigated Area Map (1999) using remote sensing through advanced Methods*
Thenkabail P.S.1, Biradar
C.M.1, Turral H.1, Noojipady, P.1,
Li, Y.J.1, Vithanage, J.1,
Dheeravath, V.1, Velpuri, M.1, Schull M.2,
Cai, X. L., 1, Dutta, R1
1International Water Management Institute 2Boston University
Abstract
A Global irrigated area map has been produced for a nominal
year of 1999 using multiple satellite sensor and secondary data. Multiple resolution
time series data used in the study were: (a) AVHRR 4-band and NDVI 10-km
monthly time series for 1981-1999, (b) SPOT vegetation NDVI 1-km monthly time
series for 1999, and (c) East Anglia University Climate Research Unit Rainfall
50-km monthly time series for 1961-2000. Additional major global data sets used
were (a) GTOPO-30 1-km elevation, (b) JERS SAR data for the rainforests during
two seasons in 1996, and (c) University of Maryland Global Tree Cover 1-km data
for 1992-93.
A number of new methods and techniques were developed. The
study first segmented the world into climate and elevation zones and analyzed
satellite images separately for these zones. The class identification and
labeling process begins with spectral matching technique (SMTs). Since
time-series data are analogous to hyperspectral data, we adopted hyperspectral
analysis techniques such as SMTs to identify, group, and label classes with
similar time series characteristics. The time-series spectra of classes were
also compared with the target ones obtained from ground truthed locations. The
spectral correlation similarity was found to be the most useful spectral
matching technique (SMTs). The SMTs are followed by selection of 30-50 random
spots for each class that are spatially well distributed and linking them to
“zoom in” view of Google earth images for which the resolution varies between
sub-meter to 30-meter. In addition ESRI 150-m Landsat Geocover mosaic of the
World, a host of image interpretation techniques such as bispectral plots,
space time spiral curves (ST-SCs), time-series plots of normalized difference
vegetation index (NDVI), and a host of secondary data (e.g., National and
global land\use and land cover data) were used. A wide array of ground truth
data were extensively used in identifying and labeling classes. First, IWMI’s ground truth data of the World with nearly 2000 points that included three missions in
2004 and 2005 covering entire India, extensive data from the river basins with
vast irrigation such as in the Ganges in India, Krishna in India, Ruhuna in Sri
Lanka, Syr Darya in Central Asia, and Limpopo in Southern Africa, and a past
data catalogue from Middle East, and 14 Countries in West Africa. Second, data
sourced from the Degree Confluence Project with about 4000 points that collates
land use data for 1 by 1 degree tile over the globe. In addition nearly 11,000
“zoom in views” of high or very high resolution Google earth points. Decision
tree algorithms, NDVI time series plots, NDVI thresholds, principal component
analysis, unsupervised clustering algorithms, and GIS spatial modeling using
data such an agroecological zones, temperature, precipitation,
evapotranspiration, and elevation were widely used to define and refine classes
especially to resolve mixed classes.
A 28-class dis-aggregated global irrigated area map at
10-kilometer scale (GIAM10km-28classes) and aggregated 8-class and 3-class
(GIAM10km-8 classes and GIAM10km-3 classes) maps of the world were produced.
The GIAM10km-28 classes (Figure 39) provide information on watering method
(irrigated or rainfed agriculture), irrigation type (surfacewater, groundwater,
and conjunctive use), irrigation intensity (single, double, or continuous
crop), and crop type or dominance. The GIAM10km-8 class provides watering
method, irrigation type, and intensity. The 3 GIAM10km-3 classes provide
information on: surfacewater irrigation, ground water irrigation, and
conjunctive use (surface and ground water) irrigation. Informal (e.g., small
reservoirs, tanks, and groundwater) irrigation was identified and mapped in
addition to more conventional large scale surfacewater irrigation found in most
irrigated area maps. Annualized irrigated areas (intensity of irrigation) were
calculated using time-series satellite imagery from which one can detect how
many crops are grown in a same area during a given year. Particular strengths
of this work are in: (a) establishing seasonal and annualized irrigated areas
(or intensity of irrigation), (b) mapping informal (e.g., small reservoirs,
tanks, groundwater) irrigation in addition to conventional surfacewater
irrigation, (c) determining irrigated crop calendar, (d) studying historical
(e.g., last 20 years, every month) biomass dynamics for every irrigated area
class and every pixel within that class. In addition, it must be noted that
this is the first satellite sensor based irrigated area map of the world. The
ability of remote sensing to map at various scale or pixel resolutions has been
demonstrated and highlighted.
The irrigated areas in these maps were calculated based on
sub-pixel areas (SPAs). The SPAs, which are areas actually irrigated, were
established by multiplying the full pixel areas (FPAs) of the classes with the
irrigated area fractions (IAFs) established based on: (a) Google earth estimate
(GEE), (b) high resolution imagery (HRI), and (c) sub-pixel decomposition
technique (SPDT). The combined coefficients from the IAF-HRI and IAF-SPDT for
each of the 28 GIAM classes were used to compute robust and reliable estimates
of the seasonal and annualized irrigated areas of the world. The annualized
areas are summation of areas from different seasons. Cropping calendar (i.e.,
single, double, or continuous cropping) for each of the 28 classes were
established and their SPAs for each of the season were determined by
multiplying the FPA with the combined IAFs from HRI and SPDT. The annualized
area is then the sum of the areas from different seasons. For GIAM this was sum
of areas from seasons consisting of single, double, or continuous cropping. The
IAF-GEE method provides total area available for irrigation (TAAI).
The annualized irrigated areas of the world at the end of
the last millennium were 480 Mha. Of which there was: (a) 263 million hectares
(Mha) for season 1, (b) 176 Mha for season 2, and (c) 41 Mha for continuous
crops. The total area available for irrigation (TAAI) at any given time at the
end of last millennium was 412 million hectares of which different proportion
of areas are irrigated during different seasons as reported above, leading to
an annualized area. The distribution of irrigated areas is highly skewed
amongst continents and Countries. Asia accounts for 78 percent of all
annualized irrigated areas, followed by Europe (8 percent) and North America (7 percent). South America (4 percent), Africa (2 percent), and Australia (1 percent) have very low proportion of the global irrigation. China has 111 Mha and India has 101 Mha of total area available for irrigation. In this 98 Mha; China has 75 Mha of crops during season 1, 68 Mha during season 2, and 7 Mha during season
3 for a annualized sum of 151 Mha. India has annualized sum of 132 Mha, with a
break up of 72 Mha during season 1, 53 Mha during season 2, and 5.9 Mha during
season 3.China and India have a staggering 59 percent of the Global annualized
irrigation. This is followed by USA (5.06 percent), Russia (3.49 percent), and Pakistan (3.32 percent). Eight other Countries have areas between 1 to 2 percent. All other
Countries in the World have less than 1 percent area irrigated relative to
global annualized total.
The accuracies of the irrigated areas were determined using
three independent datasets: (a) first, a 1861 ground truth data points of the
world sourced from degree confluence project, (b) second, a 890 point ground
truth data collected by GIAM team, and (b) third, a randomly picked 670 point
“zoom in views” of very high resolution imagery from Google earth. From these 3
methods, the accuracies varied between 84 to 91 percent with errors of omission
of not exceeding 16 percent and errors of commission of less than 21 percent.
The IWMI Global irrigated area map (GIAM) 28-class
(GIAM10km-28 classes), 8-class (GIAM10km-8 classes), and 3-class (GIAM10km-3
classes) maps, data and products are made available through a dedicated web
portal: http://www.iwmigiam.org.
These products are supported by class characteristics (e.g., cropping
calendar), snap-shots of higher resolution imagery, time-series animations of
classes showing their biomass dynamics for last 20 years, area estimation
methods, accuracy assessment results, ground truth data links for classes
including digital photos, source images, and background documentation on
methods and materials. In addition to GIAM, data and products are also
available for: (a) a Global Map of Rainfed Cropland Areas (GMRCA), (b) a Global
Map of land use/land cover areas (GMLULCA), and (c) a generic IWMI 951-class
Global land use/land cover (LULC) Map of the World.
Corresponding
author: p.thenkabalil@cgiar.org
Global map of irrigation areas 4.0 -
mapping irrigated areas by combining sub-national statistics
and geo-spatial data.
Stefan SIEBERT1, Jippe HOOGEVEEN2, Petra DÖLL1, Jean-Marc FAURES2, Sebastian FEICK1 and Karen FRENKEN2
1 University of
Frankfurt (Main), Institute of Physical Geography, Germany
2 Food and Agriculture
Organization of the United Nations, Land and Water Development Division, Rome, Italy
Abstract
A new version of a digital global
map of irrigation areas was developed by combining irrigation statistics for 26
909 sub-national statistical units and geo-spatial information on the location
and extent of irrigation schemes. The difference to map version 3 is the
incorporation of a map update for Africa, Europe and parts of Latin America.
The map shows the percentage of each 5 arc minute by 5 arc minute grid cell
(about 86 km² along the equator) that was equipped for irrigation around the
year 2000. It is thus an important data set for global studies related to land
and water, but also for assessments on food security or to quantify possible
impacts of climate change on agriculture. The article describes the data set
and the mapping methodology and gives an estimate of map quality at the scale
of countries, world regions and the globe. Two indicators of map quality that
take into account the geospatial information density were developed for this
purpose. The main results of the study are, that 278.8 Mio ha were equipped for
irrigation at the global scale. About 68% of the total irrigated area is
located in Asia, 17% in America, 9% in Europe, 5% in Africa and 1% in Oceania. The largest contiguous areas of high irrigation density are found in North India
and Pakistan along the rivers Ganges and Indus, in the Hai He, Huang He and
Yangtze basins in China, along the Nile river in Egypt and Sudan, in the Mississippi-Missouri
river basin, in parts of California, in the Po river plain in Northern Italy
and along the lower Danube. Smaller irrigation areas are spread across almost
all populated parts of the world. At the global scale, the overall map quality
is good, but there are large regional differences of map quality. At the level
of world regions, map quality in North America (overall mark 1.03), Southern
Europe (1.35), Oceania (1.44), Northern Africa (1.46), Southern Africa (1.50)
and Central Asia (1.63) is best. Western Africa (2.90) and the Russian Federation (4.00) have the worst map quality. About 65 Mio ha of areas equipped for
irrigation are located in countries where map quality is estimated to be very
good, 187 Mio ha in countries with good map quality, 21 Mio ha in countries
with fair map quality and 5 Mio ha in countries with poor map quality. Map
regions of very poor map quality do not exist anymore at the country scale.
Consequently about 90% of the total irrigated area of the world is located in
countries where the map quality is assessed to be very good or good. It was
found that remote sensing based inventories report higher values for the global
extent of irrigated land and that there is a need for a systematic comparison
of the different data sets.
Keywords: irrigation, irrigation map, global map, water use, agriculture, crop
production, land use, land cover, crop management
Corresponding
author: s.siebert@em.uni-frankfurt.de
Mapping irrigated agriculture over
the Continental US using multi-temporal MODIs data
Mutlu Ozdogan1* and Garik
Gutman2
1 NASA/GSFC, Code 614.3,
Greenbelt, MD 20771, USA
2 Garik Gutman, NASA/HQ,
Code SMD, 300 E Street SW, Washington, D.C. 20546, USA
Abstract
Accurate information on
irrigation extent is fundamental to many aspects of the Earth Systems Science
and global change research. These include modeling of water exchange between
the land surface and atmosphere, analysis of the impact of climate change and
variability on irrigation water requirements/supply, and management of water
resources that affect global food security. However, the current extent of irrigated areas over
continental to global scales is still uncertain and available maps are derived
primarily from country level statistics and spatialized using maps that are
often outdated. Even in locations, such as the US, where general extent of
irrigated areas are known, irrigation-related information exists only in
disparate datasets and cannot be easily synthesized into a single continental
scale database.
To overcome the
shortcoming of existing datasets, we developed an irrigation mapping
methodology that rely on remotely sensed inputs, better classification
methodology, and ever increasing continental and globally extensive ancillary
sources of gridded climate and agricultural data. More specifically, we use
multi-temporal data from the MODerate Resolution Imaging Spectroradiometer
(MODIS) instrument to characterize the distribution of irrigated lands over the
Continental US at 1 km spatial resolution circa 2002. Development of this
mapping methodology is part of a broader effort to map irrigation over the
entire globe.
We take a binary (i.e.
irrigated vs. non-irrigated) supervised classification approach to the
irrigation mapping problem using a non-parametric decision tree algorithm. To
help better characterize irrigation, we introduce climate-based irrigation
indices that provide precursory information on irrigation occurrence along with
existing datasets on agriculture presence. We also use remotely-sensed
temporal and spectral indices that maximize the irrigation-related
information. Two characteristics of irrigation that are observable with
remotely-sensed measurements play a particular role in determining irrigation
presence: a) temporal evolution of vegetation greenness as detected by NDVI;
and b) water stress detected by spectral indices that are most sensitive
chlorophyll presence.
Implementation of our
irrigation mapping procedure over the Continental US reveals a high spatial
resolution map of irrigated areas with expected patterns. For example, there
is a strong east-west divide in irrigation presence, most irrigated areas
concentrated on the arid western portion of the country along dry lowland
valleys such as the Central Valley of California or flat plains such as the
Texas Pan Handle. The final binary irrigation map product has a better than 80
percent classification accuracy with western portion of the country having
slightly better estimates than the eastern portion. Preliminary investigation
of estimating subpixel proportion of irrigation using remotely-sensed surface
temperature measurements over those pixels only classified as irrigated reveals
a moderate but consistent signal with the same east-west divide.
Corresponding
author: ozdogan@hsb.gsfc.nasa.gov
Irrigated Area Mapping for China - Challenge and Feasibility
Songcai YOU
Inst. of Geog. Sci. & Natural
Resources Research
Challenges
The challenges to map irrigated area in China come from data shortage, poor data quality, complex cropping system and various
irrigation intensity in different regions.
Feasibility
Feasibility in this study is expressed as data availability,
knowledge capacity and technical facilities.
(1) Data Availability
- Remote sensed data: TM/ETM images covering whole
China as of late 1980s is provided, free of charge, by GLCF, according to the
MOU signed between Institute of Geographic Sciences and Natural Resources
Research (IGSNRR) and GLCF on Sept 3, 2005. (http://glcf.geodata.cn)
- Cropping system data/map and irrigation
intensity information, provided by experimental stations affiliated to IGSNRR
in the case study area
- Land use map: at a scale of 1:100,000~1,000,000,
updated every other 5 years by IGSNRR (http://www.resdc.cn).
- Statistical data: Data Center for Resources and
Environmental Sciences in IGSNRR has started data collection and compilation
for over two decades, large amount of agricultural statistical data is
available now (http://www.data.ac.cn/index.asp)
(2) Technical Facilities
IGSNRR is strong in GIS technique application, especially
ARC/GIS (http://159.226.115.50/echannel/aboutus/eintroduction.asp) and
SuperMap, the latter is completely developed by IGSNRR
(http://www.supermap.com/)
(3) Knowledge Capability
IGSNRR is a leading research organization in geographical
sciences and resources management as well as an education body in China (http://english.igsnrr.ac.cn/). Currently, there are over 500 employees and nearly
600 students (Master and doctoral course and post-doc)
Irrigated Area Mapping Activities
To overcome above mentioned difficulties, remote sensed data
will be fully applied in irrigated area mapping in China under the support of
GIS and indigenous knowledge.
(1)
Study Area
North China Plain with an area of 300,000 km2 in China, including Beijing, Tianjin, Hebei, Henan, Shandong, Anhui and Jiangsu, is chose as case study
area, because agricultural production in this region highly depends on
irrigation.
(2) Technical Approaches
RS data is used to extract irrigated
area under the support of GIS techniques. Indigenous knowledge will be used to
help the interpretation during RS data processing and to determine the
irrigation intensity in different areas. Land use map is used to distinguish
rainfed land especially rainfed paddy land from irrigated land.
Corresponding
author: yousc@igsnrr.ac.cn
Anticipated Outputs
The final output is an irrigated area distribution map at a
scale of 100,000 with properties such as percentage of irrigated area at each county,
contribution of irrigated area to crops production in percentage, irrigation
intensity, the potential increase of irrigated area taking into consideration
of water resources availability, development and application of water-saving
irrigation techniques and changes of land use.
Outline:
Part
1 Irrigation and irrigated area mapping by
statistical data, including irrigated land and its contribution to food
production
Part
2 Application of high water efficiency irrigation
techniques in China, including ground irrigation/facility irrigation or formal
irrigation/informal irrigation
Part
3 Agricultural water demand and usage, including
historical facts and future tendency by taking into consideration
of cropping system and irrigation intensity
Part
4 Impacts of agricultural water usage to
environment, including over-exploration and pollution (environment and
ecosystem) , formal and informal irrigation
Part
5 Water management policy – review of water policy
Part
6 Irrigation in pasture (it imposes terrific
impacts on environment and ecosystem in semi-arid region, but I quite
hesitate to step in, as there exists very limited reports and papers)
Part
7 Application of RS data in thematic mapping
Corresponding
author: yousc@igsnrr.ac.cn
Estimating spatio-temporal patterns
of continuous Paddy field cover
using MODIS time series
Wataru Takeuchi
University of Tokyo
Abstract
Two thirds of the rice-growing areas in the World are in
Asian countries and hundreds of millions of people depend on rice as their
staple food source. At the same time, paddy fields have been considered to be
one of the likely and most important sources of atmospheric methane since the
rapid increase in atmospheric methane was recognized in the early 1980’s. The
improved understanding of paddy field distribution at large spatial
scales has increased the interest in deriving crop yield and methane emission estimations.
Nevertheless, the collection of such data through field surveys is
time-consuming and expensive in Asian regions. Remotely sensing data from
satellite images provide an alternative means of obtaining paddy field
distribution. In this study, the patterns observed in metrics calculated for
six month of MODIS over Japan is examined. Four analytical approached are used;
calculation of temporal mean, maximum and minimum layers for selected metrics
showing significant spatial variability of channel 1, 2, NDVI; linear
discriminant for input into the spectral mixture analysis is derived from the
same multi-temporal metrics used for the classification product using ASTER;
the continuous percentage of paddy field is generated using spectral mixture
analysis with the training data derived from the above mentioned ASTER data.
The derived metrics are not sensitive to time of year or the seasonal cycle and
can limit the inclusion of atmospheric contamination. The comparison of 250 m
MODIS product with the past efforts on 1 km AVHRR derived IGBP-DIS product
shows that the finer resolution and its un-mixing played a crucial role in
depicting the paddy field cover over Japan
Corresponding
author: wataru@iis.u-tokyo.ac.jp
Irrigated
Areas of India based on Satellite Sensors and National Statistics: Issues and
Way forward from Global Irrigated Area Mapping (GIAM)-2006
Obi Reddy P. Gangalakunta1, Prasad, S. Thenkabail2, Chandrashekar Biradar2, Venkateswarlu Dheeravath2,
Praveen Noojipady2, Manohar Velpuri2 and Muralikrishna
Gumma2
1Natioanl Bureau of Soil Survey and
land Use Planning (ICAR), Amravati Road, Nagpur, India
2International Water Management Institute
(IWMI), Headquaters, Colombo, Srilanka
Abstract
Irrigated
lands contribute significantly to the world agriculture output and food supply.
Estimates in 1986 indicated that about half of the increase in agricultural
production in the last 35 years had come from irrigated land, about one-third
of the world’s crops were grown on the one-sixth of the cropped area which was
irrigated. United Nation’s predictions of global population increase to the
year 2025 require an expansion of food production of about 40-45 per cent.
Irrigation agriculture will be an essential component of any strategy to
increase the global food supply. Growth of irrigated land is expected to occur
mainly in developing countries, increasing their share from about 80 to 90 per
cent of the world’s irrigated land. Recent work on Global Irrigated Area
Mapping (GIAM) by International Water Management Institute (IWMI) showed that
the total area available for irrigation (TAAI or net area) for the world is 412
million hectares, a dramatic increase from meager 8 million hectares in early
1800’s. The same study showed that TAAI or net area for India to be between 99 to 105 million hectares. India, with a geographical area of nearly 328 million hectares, experiences heterogeneous climatic
conditions with an annual average rainfall of 1170 mm. Normal annual rainfall
varies from 100 mm in western Rajasthan to over 11000 mm at Cherrapunji in
Meghalaya and high seasonal variability from season to season have the
tremendous impact on irrigation areas. The major sources for irrigation in the
country are classified as canals, tanks, tube wells, open wells and other
sources. As per the Bureau of Economics and Statistics-2002 estimates the gross
irrigated area in the country increased from 22.6 to 76.3 million hectares from the year 1950-51 to 2000-01
and in the same time the net irrigated increased from 20.9 to 57.2 million hectares.
Information on spatial
distribution of irrigated areas and their dynamics are desirable for the
planning, management and monitoring programmes at national, regional and local
levels for agricultural development. With increase in spatial, spectral and
temporal resolutions of the satellite sensors, medium to high resolution
satellite data provides valuable information on location, spatial distribution
and extent of irrigated areas in the country for accurate mapping of irrigated
areas and to analyze their spatial-temporal dynamics in GIS environment with
suitable spatial modeling. In heterogeneous irrigated
area mapping, the time series NDVI indices derived from NOAA AVHRR 10km, MODIS
(Moderate Resolution Imaging Spectroradiometer) 500m resolutions, national
statistics and ground truth data play a crucial role. Initially generic classes
of land use/land cover are needed to be generated using unsupervised
classification for further aggregation on various parameters. In area
estimation, the techniques like irrigated fractions and total irrigated area
for each class need to be estimated using ground truth data, national
statistics and google earth imageries. In this direction, irrigated area maps
have been produced by IWMI at 10km and 500m spatial resolution using NOAA AVHRR
and MODIS data respectively. The challenge is to study these maps in
association with Indian national statistics for further refinement. Discussions
are underway between the Indian Council of Agricultural Research (ICAR) and
IWMI to study and strengthen the irrigated area maps of India generated in GIAM project by IWMI through further refining in conjunction with
national statistics. The overarching goal will be to produce accurate and
agreeable maps and products that will be invaluable in national planning for
sustainable land and water resources.
Key words: Irrigated area mapping,
Irrigation sources, MODIS, National statistics, NOAA AVHRR, NDVI indices
Corresponding
author: obireddy@nbsslup.ernet.in
Irrigated
Areas of India through Synergy between Satellite
Sensors data and National Statistics
Obi Reddy P. Gangalakunta
Natioanl
Bureau of Soil Survey and land Use Planning (ICAR), Amravati Road, Nagpur, India
1. Introduction
2.
General Description and Background
2.1 Geographical settings of India
2.2 Climatic and rainfall patterns in India
2.3 A history of irrigated areas of India
3. General land use pattern: Existing knowledge base
3.1 Land use pattern in the country
3.2 Major cropping patterns in the country
3.3 Irrigated areas in the global context
3.4
Historical background of irrigation system
3.5 Major Irrigation sources and their dynamics
3.6 Trends in irrigated areas
4.
Methodology
4.1 Collection of National statistics
4.2 MODIS, LANDSAT and IRS data analysis
4.3 Sensors data and national statistics
5.
Satellite sensors data and National Statistics
5.1 National statistics on irrigated areas
5.2 Satellite sensor data at national scale
5.3 Validation of Irrigated area maps with national statistics
5.4 Refinement of irrigated area maps
6. Issues
and way forward
6.1 Irrigated area mapping and scales
6.2 Analysis of dynamics and composition of irrigation sources
6.3 Analysis of Irrigated areas in association with LGP
6.4 Analysis of changes in irrigated areas
6.5 Irrigated areas and water use efficiency
6.6 Analysis of cropping systems and cropping intensity
6.7 Irrigated areas and yield gap analysis.
6.8 Prediction of near future Irrigated areas changes in GIS.
6.9 Simulation of scenarios of irrigated areas
6.10 Analysis of impacts on Irrigated areas
6. 11 Identification of critical areas for judicious use of
irrigation water
6. 12 Assess
and estimate the potential irrigated areas
Corresponding
author: obireddy@nbsslup.ernet.in
Mapping the spatial distribution of
irrigated areas and volumetric water demand in a temperate climate: a case
study in England and Wales
J.W. Knox * and E.K.
Weatherhead
Institute of Water and Environment, Cranfield University, Silsoe, Bedford, MK45 4DT, UK
Abstract
In England and Wales, irrigation is supplemental to rainfall
but concentrated on high value crops such as potatoes, vegetables and soft
fruit, where reliable, continuous supplies of premium quality produce are
demanded by the major supermarkets. Demand for irrigation is rising steadily,
peaking in the driest years and in the driest catchments when water resources
are most limited. New water regulation and changes in resource management and
abstraction licensing are currently being implemented by the water regulator
(Environment Agency) to address concerns regarding the sustainability of water
withdrawals, and the potential impact that over-abstraction is having on the
water environment. Increasing competition between sectors (industry, public
water supply and agriculture) coupled with the longer-term threat of climate
change will exacerbate the situation, with reduced summer river flows and
increases in water demand being predicted. New detailed baseline information
showing the temporal and spatial the extent of the areas irrigated and volumes
of water abstracted for agricultural irrigation would therefore be useful for
informing decision-making by water resources planners and water policy advisors
seeking to redress the balance between the needs of abstractors with that of
the water environment.
A procedure has been developed to model and map the spatial
distribution of the irrigated areas and the volumetric irrigation water demand
in England and Wales. The methodology uses a data-bridge approach to combine
high resolution digital datasets relating to soils, agroclimate and land use
within a geographic information system (GIS), with outputs from a daily water
balance irrigation scheduling model and data derived from a national survey of
irrigation. Maps showing the spatial extent of the areas irrigated (ha) and the
theoretical irrigation water demand (m3), by crop type and in total,
in a ‘design’ dry year have been produced.
The GIS mapping outputs have been aggregated for use at a
range of levels, from region to local (sub-catchment) scales. A brief
description of the individual components of the modelling procedure are
provided. The integrity of the datasets used, the problems relating to error
propagation and the statistical accuracy of the irrigation survey data are then
discussed. The future application of the GIS modelling outputs in support of
improving the management, allocation and planning of water resources for
irrigated agriculture (with and without climate change) are highlighted.
Keywords: England and Wales; GIS; Irrigation; Maps; Prediction; Water demand
* corresponding author: j.knox@cranfield.ac.uk
Irrigated area in India over the last 50 years: Past expansion and present trends
A. Narayanamoorthy
Gokhale Institute of Politics and
Economics (Deemed University), Pune, India
Abstract
India’s irrigation sector is one of the largest in the world,
both in terms of irrigated area and the volume of investment. Government alone
has invested about Rs. 1556.25 billion (in current prices) up to 2001-02 in
irrigation sector. As a result, the irrigated area of the country increased
from 20.85 million hectares in 1950-51 to 78.38 million hectares in 2001-02, an
increase of nearly four times. Though a large number of studies have analysed
the impact of irrigation on various developmental parameters, not many studies have
looked at the development of irrigation across major sources as well as across
states using time series data from 1950-51 to 2002-03. The trends in
development of irrigated area at the country level may not be the same across
the states owing to various reasons. Similarly, among the three major sources
(tank, canal and groundwater) of irrigation, the development may not be the
same across the states. In this study, therefore, an attempt will be made to
study the past development of irrigated area across the states using time
series data. Specifically, the study will address the following aspects of
irrigation: (a) Irrigation potential created up to 2001-02 in relation to
ultimate irrigation potential of the country as well as different states, (b) Expansion
in irrigated area in absolute term as well as its share in terms of net sown
area and gross sown area, (c) Expansion in irrigated area by source (d) Growth
pattern of irrigated area by source at different periods. (d) Impact of
irrigation (by source) expansion on cropping intensity. While descriptive and
growth analysis will be used for this study, the study would cover all the
major states for its analysis.
Corresponding
author: na_narayana@hotmail.com
Irrigation potential
creation and realisation
V.Venkateshwar Rao
Water Resources Division, National
Remote Sensing Agency (NRSA), Hyderabad, India
Abstract
Irrigation development has been accepted as a
major factor in increasing agricultural production. Irrigation forms the datum
line for sustained successful agriculture. The massive development of a vast
irrigation network in India has been recognised as a landmark in the history of
agricultural development anywhere in the world. Ultimate irrigation potential
in the country is estimated at 139.89 million ha, comprising of 58.46
M ha through Major and Medium irrigation and 81.43 M ha( 64.05 M ha from groundwater
and 17.38 M ha from surface water) from Minor irrigation. Additionally, the
inter-basin transfer of water from surplus to deficit basins is being pursued
by Government of India is expected to bring 35 M ha under irrigation. From
1951 to 2002, gross irrigated area (GIA) expanded more than four fold, from
22.6 M Ha to 93.96 M ha contributing to the growth in the overall cropping
intensity from 111 % in 1950-51 to 132% in 2001-02 . While enormous irrigation
potential of 99.36 M ha has been created at huge cost, the gap between created
potential and utilisation is significantly large around 14 M. ha till the end
of March,2005.
In India, estimates of
UIP are not based on any river basin wide planning or survey .Seasonal
imbalance in flow of rivers, geographic incongruity between regions with
undeveloped water potential and those with irrigable lands; increasing
competition for land and water from non irrigation sector, and due to non -
conjunctive assessment of surface and groundwater are some of the factors
leading to such questionable estimates. In addition to these, there are
differences in the interpretation of the concept of IP creation and utilisation
by the reporting agencies in the country. The system of monitoring and
verifying information provided by executing agencies on both potential and
actual irrigation is inadequate and casual and there are substantial reporting
and compellation errors in the data.
Poor water use
efficiency, low productivity and poor sustainability and land degradation
(salinity and water logging) are limiting factors in water utilisation pattern
in India. Conventional methods of irrigation management are based primarily on
unreliable data bases, with considerable time lag in their generation, trial
and error approaches and operator experience. Now methods which use computer
based capabilities of data collection, management, analysis and decision
support are, therefore, needed to increase the efficiency of irrigation system
operation.
A well-developed standardized national
information system, with databases and networked data banks, integrating and
strengthening the existing Central and State level agencies, helps
ratoinalising the irrigation data bases across the country is the need of the
hour.
A conceptual frame work is proposed in this
paper taking into account the developments in hydrologic, irrigation and
agricultural sciences, database management systems, GIS, remote sensing and GPS
facilitating aggregation of data across spatial scales. There should be a National
agenda using the frame work suggested to rationalise the irrigation potential
created and utilized. The recent initiatives in India in generating irrigated
data bases hold promise to realize such a frame work.
Corresponding
author: vvrao@nrsa.gov.in
Mapping irrigated areas of the world
using remote sensing data
Abdolreza Ansari Amoli
Iran Space Agency,Tehran,
Iran
Crop yield mapping includes Irrigated and non-Irrigated area
mapping . Geographic Information Systems (GIS) and remote sensing are two
important technologies that enable mapping of Irrigated and non-irrigated area.
The capability of data acquiring in a large area, highly potential in
time-series and online data producing, are the most important and useful
characteristics of remote sensing technology. In this regard, hyperspectral
satellite data like MODIS are specially suitable for mapping of Irrigated
area.By using MODIS data and applying different algorithms based upon plant
phenology and growing stage (Multitemporal Methods) we can discriminate the
agricultural crops by a very good precision.
I Suggest following subsections ( as Draft) for the section entitled “Mapping
irrigated areas of the world using remote sensing data”:
1.Irrigatd Area Mapping
1-1.Classical Methods
1-2.New technologies
1-2-1.Remote Sensing
1-2-1-1 Type of Data
1-2-1-1-1 10 Km Resolution
1-2-1-1-2 500m Resolution
1-2-1-1-3 30m Resolution
1-2-1-2 Methodologies
1-2-1-2-1 Classification
Old methods (include Maximum
Likelihood,Minimum Distance,…)
Genetic Methods (include Fuzzy
Classification,Neural Network,….)
Multitemporal Methods
Corresponding
author: aansari@isa.ir
Using
MODIS Thermal Data for Estimating Actual
Evapotranspiration From Irrigated Fields
Senay, G.B., M. Budde and J.P.
Verdin
USGS Earth Resources Observation
and Science (EROS)
Abstract
Accurate crop performance monitoring and production
estimation are critical for timely assessment of the food balance of several
countries in the world. Recently, the Famine Early Warning Systems Network
(FEWS NET) has been monitoring crop performance and to some extent relative
production using satellite derived data and simulation models in Africa,
Central America and Afghanistan where ground-based monitoring is limited due to
a scarcity of weather stations. The commonly used crop monitoring models use a
crop water balance algorithm with inputs from satellite-derived rainfall. While
these models provide useful monitoring for rain-fed agriculture, they are
ineffective for irrigated areas. This study has focused on Afghanistan where over 80% of the agricultural production comes from irrigated agriculture.
We implemented a simplified energy balance approach to monitor and assess the
performance of irrigated agriculture in Afghanistan using the combination of
1-km thermal data and 250-m NDVI from the Moderate Resolution Imaging
Spectroradiometer (MODIS) sensor. Up to 19 cloud free thermal and NDVI images
were used for each year to estimate seasonal actual evapotranspiration (AET)
for two major irrigation river basins (Kabul and Helmand) over 6 years
(2000-2005). Seasonal AET estimates were used as relative indicators of
year-to-year production magnitude differences. The temporal water-use pattern
of the different irrigated basins was indicative of the cropping patterns
specific to the region. The results were comparable to field reports and
watershed-wide crop water balance based estimates in that the 2003 seasonal AET
was the highest of all six years. The advantage of this method over crop
water balance methods is that the energy balance approach also helps identify
spatial extents of irrigated fields and their spatial variability as opposed to
a lumped watershed-wide assessment that can be obtained from large-scale
water-balance models.
Corresponding
author: senay@usgs.gov
Conjunctive Water use Area Dynamics
and its Mapping using Multi-temporal IRS Data
Praveen Gupta1, Sushma
Panigrahy1, Parihar, J.S1 and Subashisa Dutta2
1 Space Application Centre, Ahmedabad, India
2 Department of Civil Engineering,
Indian Institute of Technology, Guwahati, India
Abstract
Conjunctive Water use Area Dynamics and its Mapping
usingMulti-temporal IRS Data P. K. GUPTA1, S. DUTTA2, S. PANIGRAHY1 and J. S.
PARIHAR1 ABSTARCT Irrigated agriculture in many areas of the world, is
currently being practiced from multiple water sources such as precipitation,
canal, wetlands, ground aquifer, etc. Analyzing this conjunctive water use and
its dynamics is an important aspect for sustainable water resource management.
This chapter highlights the use of multi-scalen, multi-temporal remote sensing
data and Geographic Information System (GIS) to analyzing the conjunctive water
use in rice cropping system area in West Bengal, India. The Methodology has
been developed and validated for the upper canal Damodar irrigation command
area, for the summer season of year 2000 and 2001. The prime objective of the
work is first to develop methodologies to derive the controlling variables of
the water use from a multi-date image stack. The controlling variables used are
relevant land use, crops grown, crop calendar, growth stages, biometric
parameters like leaf area index (LAI). High temporal resolution data like IRS
WiFS was found useful to derive most of the crop dynamic features, while high
spatial resolution data of IRS LISS III has been used to map the crop type and
landuse. A correlationship analysis between satellite-measured radiances and
field-collected LAI has been used to derive a spatial LAI distribution of rice
crop. Other controlling variables such as canal discharge schedules, daily
rainfall, wetland irrigated were spatially integrated in a geographic
information system. A decision rule based classifier has been used to identify
irrigation source and its spatial distribution in the study area. Results show
that deviation between the mapped and field-collected water use locations is
less than 5 percent. Further using all the information, daily water balance was
computed to estimate actual irrigation water use and its productive in terms of
LAI. It was found that irrigation productive of ground aquifer source is high.
Key word:
Conjunctive water use, remote sensing, LAI, reflectance, irrigation mapping
Corresponding author: pkgupta@sac.isro.gov.in
Semi-supervised technique to
retrieve irrigated crops from Landsat ETM+ imagery for small fields and mixed
cropping systems of South Asia
MSDN Gamage, Mobin-ud-Din Ahmad and
Hugh Turral
International Water Management
Institute, Colombo, Sri Lanka
Abstract
Precise land cover maps and crop statistics are essential
for monitoring and performance evaluation of any irrigation system. Remote
sensing techniques offer efficient means of obtaining land cover information
with high accuracy in near real time. Many applications developed and
referenced in the literature classify large tracts of homogenous cropped area,
and are usually less effective in highly mixed cropping systems in South Asia (Canisius, forthcoming). This paper presents a semi-supervised technique to map
cropped area in two major irrigation commands representing the Punjab
Rice-Wheat, Punjab Sugarcane-Wheat and NWFP (North West Frontier Province) Maize-Wheat cropping systems in the Indus Basin irrigation system in Pakistan. Four Landsat ETM+ images were selected to the study: two Landsat ETM+ images
(Path 149 Row 038) for September 2001 and March 2002 were selected to represent
Kharif (2001) and Rabi (2001-02) seasons of Rechna Doab in Punjab. Rest of two
images (Path 151 Row 36) of April 2002 and September 2002 were to represent
Pehur High Level Canal (PHLC) area in NWFP.
A ground truth survey was conducted in different cropping
areas that covered both irrigation areas. Accordingly geo-referenced GIS
coverages of land use land cover were prepared for image classification. As
first step, using field data and NDVI of those images, the vegetation was
segregated form non vegetation area based on threshold values. Then based on Principle
Component Analysis (PCA), Red, NIR and MIR bands were selected for supervised
classification. GIS coverages were overlaid on a stacked image and 50% of the
collected information was used to extract training signatures for all crops.
The training samples were evaluated based on their location on two scatter
plots between NIR:Red and NIR:MIR which yielded to distinct crop classes. The
signatures of these distinct crop classes were used to perform supervised
classification using maximum likelihood parametric rule. Finally, using the
classified maps and other half of the field data, contingency matrixes were
prepared to evaluate the classification accuracy in each season.
The results of Rechna Doab area show an overall accuracy of
87% in Kharif (Summer-Monsoon) compared to 83% in Rabi (Winter-Dry). Fodder
signature mixed up with wheat causes to comparatively low overall accuracy in
Rabi even though the lesser diversity of crops within the season. The results
from the PHLC area give an overall accuracy of 78% in Kharif and 85% in Rabi
season. Comparatively higher classification accuracy in Rechna Doab, especially
in Kharif season, is due to more representative ground truth data, and large
and homogenous area under paddy crop.
Keywords: Remote Sensing, GIS, Crop Classification, Land use-Land cover,
Spectral Mixture, Pattern Recognition, Mixed Cropping System, Irrigation, Pakistan.
Corresponding author: a.mobin@cgiar.org
Assessment of availabilities and
demands of water resources in river basins
Geerken, R. and Smith, R.
Department of Geology and
Geophysics, Yale University, New Haven (CT) 06520, U.S.A.
Abstract
The regional modeling of hydrological characteristics of
watersheds is currently limited to some basic input parameters that are
globally available. Though, more variables may be locally measured at a regular
basis, consistency in the input parameters is advisable where comparability of
results is required. For data sparse regions we developed a simple water
balance model that takes account of the limited availability of data with
regional coverage. Input parameters are rainfall, temperature, and topography.
Soil moistures are computed at 10-day intervals to show seasonal and spatial
soil moisture/snow/run off variations over a time range from 1994 to 2004
(1981-2000). Through integrated analyses of modeled soil moistures with NDVI
data from 8-km AVHRR (1981/1994-2000) and SPOT (1999-2004; radiometrically
adjusted and spatially degraded) we identify locations and periods with crops
under irrigation as well as inter-annual changes and trends in irrigation
patterns. Model outputs further allow a characterization of the landscape with
regard to their ecological potential or their vulnerability.
Using examples from the Middle East and from Central Asia we
use these methods, e.g., to visualize the increasing irrigation water demand
along the Euphrates River, the inter-annual response of irrigated agriculture
to climate variation, or the impact of climate change on the seasonal
availability of water resources.
To further improve the mostly qualitative model outputs, and
add vegetation characteristics as an important component to the hydrologic
modeling, we developed a Fourier based vegetation classification scheme of
spatial and temporal compatibility. Class assignment is decided by a vegetation
types’ phenological cycle but also measures its vegetation coverage.
Classification results represent a highly consistent clustering of
“phenologies” (NDVI-cycles) according to vegetation type, to land management
(e.g. double/single crop), and to their coverage or, in multi-temporal
analyses, quantifiable changes in these parameters. Multi-temporal analyses
using classification results and hydrologic model outputs are used to analyze
land cover/land use changes and inter-annual fluctuations/changes in water use
efficiency.
Finally, initial steps are discussed towards a consistent
parametrization of hydro-meteorological vegetation variables derived from the
Fourier based classification, intended to enable the modeling of interactions
and feed backs between vegetation and the hydrological cycle.
Corresponding author: roland.geerken@yale.edu
Farmers’ Lead Participatory Research
For Scarce Natural Resource Management In Karnataka
Gangadharappa, N.R and
Ganesamoorthi,S.
University of Agricultural Sciences,
Bangalore – 560065, India
Abstract
The command areas are facing water efficiency problem
because of upstream farmers siphoning out large volumes of water by adopting
water intensive cropping pattern, creating land degradation problems and water
scarcity at tail-end. This is the greatest hurdle in reaching possible
irrigation potential of 3.5 m.Ha in Karnataka and 0.29 m.Ha in Hemavathy
Command Area. The pursuit of maximizing productivity of land at the cost of
optimizing productivity of scarce water resource has defeated the very
objective of huge public investments on irrigation structures. Prior to
independence, the local institutions had responsibility of maintaining and
monitoring the resources. Now the same is managed by the Government which lacks
manpower and resources, causing increased problems of maintaining and
monitoring a wide network of irrigation systems. Hence, Government of Karnataka
through state water policy has mooted the formation of Water Users Association
(WUA) in the Command Areas to encourage the active participation of the end
users and reviving the tradition of collective management during the year 2002.
During this time, participatory action project was initiated through one of the
identified informal WUA in Bagevalu village considering massive scarcity to
share the water, managing and maintaining the structures in addition to the
analysis of experiences of existing informal organizations.
Personal interviews, dialogues, village-stays, Participatory
Rural Appraisal techniques, field visits and discussion with the concerned
stakeholders of Hemavathy Command Area were proceeded to map the informal
organisation and identify the research location for conducting participatory
research. The analysis of eight informal organisations revealed that they were
engaged in sharing canal irrigation water during the crisis without having
their own organisational structure and resources. These organisations used only
“discussion cum persuasion techniques” with fellow stakeholders to share water.
Thus, they gave importance to social sustainability. “Manipulation by powerful
elite farmers”, “biased bureaucratic approach”, ‘violation of recommended
cropping pattern”, “ill maintenance of physical structures” and “wastage of
water” were the problems faced by these organizations in sharing water. Then
participatory action project started with mobilization of all stakeholders to
become the members of this association by paying membership fee. After
completing cent percent, farmers were facilitated for its registration. The 982
stakeholders of this association were spread along the five distributaries. The
repair works of the physical structures were carried out jointly by the
Irrigation Department, Command Area Development Authority and the Bagevalu WUA.
“Proper and judicious use of available canal irrigation water in an equitable
way among all stakeholders through empowerment of people” was the principle
used. The capacity building and field level participatory extension activities
were organised for the members intensively during the next two years on water
use efficiency and recommended cropping pattern. The impact assessment made
during the year 2004 revealed that “groups and networks”, “trust and
solidarity”, “information and communication”, “collective action and cooperation”,
“social cohesion and inclusion” and “empowerment and action” between the
stakeholders have improved and they changed crop from paddy to light irrigated
crops. Minimal efforts of social capital development have responded favourably
to manage the water productively.
Corresponding author: nrganga@yahoo.co.in
Irrigated areas of Pakistan over last fifty years
Rakshan Roohi
Water Resource Research Institute, Pakistan
Abstract
Pakistan is inherently situated in a predominantly semi-arid
to hyper-arid climatic zone. The Indus River System (IRS) is the main source of
water for agricultural and non-agricultural water uses. It has three super dams
besides 68 other large dams, 23 barrages/headworks/siphons, 12 inter-river link
canals, 45 huge canal commands, more than 107,000 water courses and over
600,000 tube wells.
The sources of water are surface
water (55%), groundwater (40%) and rainfall (5%). The catchment area of IRS
spread over a vast tract of 500,000 sq. km out of which 56 percent lies within
the country boundary. The catchment includes three major mountain ranges namely
Himalaya, Karakoram and Hindukush (HKH) having variable snow and glaciated
cover. Glaciers and snow melt contributes on an average 67.5% of the total IRS
flows, ranging from 85% of Indus flows to little over 50% of Jhelum River
basin. In an inventory, 5,218 glaciers have been identified having an area of
15,041 sq. km and estimated ice reserves of 2,738 km3. Considering
an ice-water conversion factor of 1: 0.9, the water reserves in this ice mass
are 1,997 MAF. The total surface water available at rim station in Indus Basin
System is only 7.44% of this huge reserve. In the current scenario of climate
change the glaciers are melting at a faster rate resulting in the formation of
glacial lakes or increase in the size of existing lakes.
The average annual flow of IRS is
approximately 144 MAF of which presently 105 MAF is being diverted for
irrigation while a major portion of the balance outflows into the sea. At
present, irrigation uses about 93% of the water and support agriculture which
contributes about 25% of GNP, more than 60% of foreign exchange earnings and
provides 90% of food and fiber requirements. About 68% of the rural population
depends on the sector and 46% of the labor force is employed in it. According
to the statistics (2003-04), the irrigated agriculture was practiced over an
area of 18.78 mha. The area under irrigated agriculture estimated by analysis
of NOAA image of October 14th, 1992 is 17.132 mha compared to the
statistics estimates of 1991-92 as 16.85 mha. The difference between two
estimates needs to be further analyzed. It can be due to SRS data resolution
and masking the total cropped area with rainfed zone or deficiencies in the
estimate procedures. Currently using Landsat TM and ETM+ data the estimation of
extent of various Landcover/landuse classes is in progress.
The population of the Pakistan was 65.3 million in1972 which has increased to 130.6 million in 1998. The per
person water availability in the country has been going down and would reduce
further from 1200 cubic meters per person to 1000 cubic meters per person by
2010. Furthermore, waterlogging and salinity pose a major threat to the
sustainability of irrigated agriculture in about 30 percent of irrigated lands,
which is directly related to the low efficiency of irrigation systems. The
other threats to irrigated agriculture include uneven distribution of water,
low storage capacity, excessive groundwater extraction and weak institutional
linkages. Considering all these factors the need of the day is to have a "Green"
as well as “Blue” revolution simultaneously for a prosperous economic
growth of the country.
Corresponding author: drroohi@hotmail.com
Satellite remote sensing
and GIS based irrigated area mapping in Godavari River Basin of India
Jayashree Shivaji
Pachpute and Dilip Dyandeo Pawar
Mahatma Phule Krishi
Vidyapeeth, Rahuri-, India
Abstract
The Mula irrigation
project is a major irrigation scheme situated in Godavari river basin of India. The overall efficiency of this project is only 38 per cent under surface irrigation
systems. This low efficiency is due to conveyance and seepage losses through
canal distributaries, minors and field channels as well as adoption of
unscientific water management practices such as over irrigation, absence of
suitable layouts for crops and lack of improved package of practices such as
timely sowing, high yielding cultivars and balanced fertilizer use in relation
to water availability. Due to lower efficiencies in water conveyance, storage
and distribution the area actually irrigated through canals is less than the
area recorded by irrigation department. The tail end farmers do not get
adequate or remain deprived of irrigation water. Therefore remote sensing and
GIS technology was used to assess the actual area irrigated with its spatial
distribution in head and tail commands. The Indian Remote Sensing Data of
RESOURCESAT P6 having resolution of 23.5 m was used for irrigated area
assessment in the command. The inventory of irrigated area was rapidly prepared
by using multi-spectral satellite images of IRS LISS III sensor for different
overpass dates. The dates of overpass were falling in rabi season during which
the moisture content of irrigated land in the study area was quite higher than
the surrounding non-irrigated land. Due to this difference in moisture content,
there was a large contrast between the spectral reflectance from the irrigated
crops and from the surrounding areas. By simple unsupervised image
classification technique, the irrigated areas were identified and their
statistics were determined. In rabi 2004-05, the irrigated command area (ICA)
of right bank canal of Mula irrigation project was 72832 ha indicating
irrigation intensity of 70.2 per cent. The irrigated area as per the official
records was 80810 ha. So a reasonable difference of 7978 ha was found in
recorded and actually irrigated area. The accuracy of irrigated area assessment
was more than 85 per cent. The NDVI profile generated from multi-spectral
imageries of different overpass dates indicated inadequacy of irrigation at the
tail end of most of the distributories in the command.
Corresponding
author: jaishree_kumkar@rediffmail.com
Multi-angle spectral measurements for classifying cropping areas
Francis Canicius
University of West Indies
Abstract Vegetation covers on the earth surface have different structures depending on their cover type. Forests may be the most highly organized structures with shoots, branches, tree crowns and tree groups, while grasses and crops are lacking such similar structures. Though the crop lands sometimes have similar greening process as herbaceous vegetation, they are homogenous and the distribution of crops is spatially arranged and therefore not random.
Multi-angle satellite observations provide means to characterize the anisotropy of surface reflectance, which has been shown to contain information on the structure of vegetated surfaces. The total reflectance measured by a single observation at nadir is largely determined by the sunlit components of foliage and it overlaps between the natural vegetation and crop lands leads to misclassification. Therefore, additional information, preferably angular as it characterizes vegetation structure, is needed for the classification. Utilizing spectral measurements over a range of observation angles, however, allow discriminating cropping areas from the pattern of variation.
The Multi-angle Imaging SpectroRadiometer (MISR) instrument on board the Terra platform offers the capability of acquiring reflectance data on any earth target in four spectral bands, from nine different directions, at a multiple spatial resolution of 250m and 1000m. One dimension fully exploits the spectral information in blue, red and near infrared bands while the other dimension capitalizes on multi-angle capability of MISR to assess the anisotropic behavior of terrestrial surfaces with respect to solar radiation.
This investigation uses MISR data to estimate land cover characteristics and classification of cropping area particularly irrigated winter wheat in northern part of India. The analyses indicate that both spectral and angular variables are significantly different for different land cover types and they all convey the information valuable for identifying land covers. In addition, the incorporation of both multi-angle and multi-spectral 250m resolution data substantially improves the classification accuracy. The emphasis of the work also assesses to what extent multi-angle data can be used to reduce the difficulties in land cover classification mainly in cropping area classification process. These new findings provide evidence to the improved capabilities for the applications of MISR data. The resolution of MISR is expected to be sufficient to classify the cropping area. Further testing has to be done for detailed discrimination of cropping systems and crop types for better understanding.
Corresponding author:
franciscanicius@yahoo.com
Mapping the irrigation area for estimation of agricultural water demand in North China Plain using MODIS remote sensing data.
Zhihao Qin1,2, Maofang Gao1 and Wilko Schweers1
1 Institute of Agro-Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Zhongguancun South Street 12, Beijing 100081, China.
2 International Institute for Earth System Sciences, Nanjing University, Hankou Road 22, Nanjing 210093, China.
Abstract
The North China Plain is one of the most important agricultural regions in China with severe challenges of water shortage. Agriculture in the plain is very intensive. Farming in the region is a typical irrigation-supported system of winter wheat, followed by summer maize. Other important crops include cotton, potatoes, soybean and various vegetables. Cultivation of these crops requires large amounts of irrigation water to support the harvest. However, water resources are very limited due to high evaporation and unbalanced precipitation. Although the average annual precipitation in the region varies between 500-800mm, water shortage has been a common social-economic problem, resulting from a rapid increase of economic development and intensive farming. Both surface and underground water resources in the region have been over-extracted to meet an ever-increasing demand, leading to omens of water scarcity disasters in the region. For example, each year the Yellow River, the 2nd largest river in China and the largest river in the region, had no water to enter the Bohai Sea for several months. The ground water level has fallen at a rate of abou |