AN ECONOMIC ANALYSIS OF INSTITUTIONAL REFORMS IN IRRIGATION SECTOR IN PUNJAB PAKISTAN By MUHAMMAD ARIF RAZA M.Sc (Hons) AGRICULTURAL ECONOMICS A THESIS SUBMITTED IN PARTIAL FULFILLMENT FOR THE DEGREE OF DOCTOR OF PHILOSOPHY IN AGRICULTURAL ECONOMICS Faculty of Agricultural Economics and Rural Sociology University of Agriculture Faisalabad 2008
211
Embed
AN ECONOMIC ANALYSIS OF INSTITUTIONAL REFORMS IN ...prr.hec.gov.pk/jspui/bitstream/123456789/55/1/73S.pdf · 1.2 Actual Surface Water Availability in Pakistan 7 1.3 Agricultural Water
This document is posted to help you gain knowledge. Please leave a comment to let me know what you think about it! Share it to your friends and learn new things together.
Transcript
i
AN ECONOMIC ANALYSIS OF INSTITUTIONAL
REFORMS IN IRRIGATION SECTOR IN PUNJAB
PAKISTAN
By
MUHAMMAD ARIF RAZA
M.Sc (Hons) AGRICULTURAL ECONOMICS
A THESIS SUBMITTED IN PARTIAL FULFILLMENT FOR THE DEGREE
OF
DOCTOR OF PHILOSOPHY
IN
AGRICULTURAL ECONOMICS
Faculty of Agricultural Economics and Rural Sociology
University of Agriculture Faisalabad
2008
i
TABLE OF CONTENTS
Chapter
No. Title Page No.
List of Tables vii
List of Figures ix
Acknowledgements x
Dedication xii
Abstract xiii
1 INTRODUCTION 1
1.1 A Brief History of Irrigation Reforms in the World 3
1.2 Agriculture and Economy of Pakistan 5
1.3 Irrigation Sector in Punjab 9
1.4 Canal Irrigation System of Punjab 10
1.4.1 Main Canal Level 10
1.4.2 Distributary Level 10
1.4.3 Watercourse Level 10
1.5 Objectives of Irrigation System in Punjab 12
1.5.1 Design Stage Objectives 12
1.5.2 Operational Objectives. 12
1.6 Issues of Irrigation Management 13
1.6.1 Low Irrigation and Water Use Efficiencies 13
1.6.2 Poor Aabiana Collection (Water Charges) 14
1.6.3 Inequitable Distribution of Irrigating Water 14
1.6.4 Inadequate Maintenance of the System 15
1.6.5 Poor Irrigation Infrastructure 15
1.6.6 Illegal Diversion from Distributaries 16
1.6.7 Inadequate Farmer‘s Participation in Irrigation
Management 16
1.6.8 Corruption and Rent Seeking Behavior of the
Officials 16
1.7 Need for Institutional Reforms in Irrigation
Sector 16
ii
1.7.1 Irrigation Management Transfer 17
1.7.2 Participatory Irrigation Management 17
1.8 PIM Model for Punjab 17
1.9 Description and Functions of PIDA, AWB and FOs 19
1.9.1 Punjab Irrigation and Drainage Authority
(PIDA) 19
1.9.2 Area Water Board (AWB) 20
1.9.3 Farmers Organizations (FOs) 20
1.10 Schedule for Formation of FOs 20
1.11 Legal Framework and Composition of PIDA 21
1.12 Need for the Study 24
1.13 Objectives of the Study 25
1.14 Summary 25
2 REVIEW OF LITERATURE 26
2.1 Selected Studies from Outside Pakistan 26
2.2 Selected Studies Related to Pakistan 41
2.3 Summary 49
3 METHODOLOGY 50
3.1 Selection of the Study Area 50
3.2 Characteristics of the Study Area 50
3.2.1 A Brief Description of the Districts in the Study
Area 51
3.2.2 Specific Characteristics of the LCC (East) 53
3.3 Sampling Framework 56
3.3.1 Sampling Size 59
3.3.2 Questionnaire Development 59
3.3.3 Pre-Testing of the Questionnaire 60
3.4 Data Sources and Collection 60
3.4.1 Primary Data Collection 60
iii
3.4.2 Secondary Data Collection 61
3.5 Data Entry 62
3.6 Cleaning and Organization of Data 62
3.7 Indicators for Performance Measurement 62
3.8 Summary 66
4 CONCEPTUAL FRAMEWORK 67
4.1 Single Equation Estimation: OLS Approach 67
4.1.1 Assumptions of OLS 67
4.1.2 General Form of the Model 69
4.2 Concept of Production Function 69
4.2.1 Cobb-Douglas Production Function 70
4.3 Efficiency 71
4.3.1 Input Oriented Efficiency Measures 72
4.3.2 Concept of Production Frontier 73
4.3.3 Measurement of Technical Efficiency 74
4.3.4 Parametric Frontier Production Function 75
4.3.5 Stochastic Frontier Production Function 76
4.3.6 Estimation of Stochastic Frontier
Production Function 78
4.3.7 Estimation of Mean and Firm-Level Technical
Efficiencies 79
4.3.8 Technical Inefficiency Effects Model 80
4.4 Summary 82
5 METHODS OF ANALYSIS 83
5.1 Approaches for Analysis 83
5.2 Quantitative Analysis 83
5.2.1 Comparison of Means, Averages, Percentages
and Frequencies 84
5.2.2 Estimation of Econometric Models for Different
Crops 85
iv
1 Estimation of Model for Gross Value Product
of Wheat 85
2 Estimation of Model for Wheat Yield 87
3 Estimation of Model for Gross Value Product
of Rice Crop 89
4 Estimation of Model For Rice Yield 91
5 Estimation of Model for Gross Value Product
of Sugarcane Crop 92
6 Estimation of model for Sugarcane Yield 94
5.3 Economic Inefficiency Model 96
5.3.1 Empirical Model and Efficiency Analysis 96
5.4 Summary 100
6 COMPARISON OF PERFORMANCE INDICATORS 101
6.1 Socio-Economic Profile of the Respondents Across the
Study Area 101
6.1.1 Social Indicators 102
6.1.2 Agricultural Indicators 104
6.2 Comparison of Indicators Developed from Primary Data
Sources 105
6.2.1 Opinion of the Farmers Regarding O&M and
Quantity of Irrigation Water 106
6.2.2 Farmer‘s Perception on Reduction in Water
Theft Cases 109
6.2.3 Average Yield of Major Crops Across the
System 110
6.2.4 Average Gross Value Product (GVP) of Major
Crops Across the System 112
6.2.5 Average Cost of Production of Major Crops
Across the System 114
6.2.6 Comparison of Gross Margin of Major Crops 124
v
Across the System in Pre and Post Reform
Period
6.2.7 Ratio of Gross Margin to Cost of Production
Across the System 127
6.2.8 Cropping Intensity in the Study Area in Pre and
Post- reform Period 128
6.3 Comparison of Indicators Developed from Secondary
Data Sources 129
6.3.1 Comparison of Aabiana Assessment and
Collection in Pre and Post-reform Period 129
6.3.2 Comparison of Per Hectare Operation and
Maintenance Expenditures in Pre and Post-
reform Period
131
6.3.3 Per Hectare Salary Expenditures in Pre and Post-
reform Period 133
6.3.4 Per Hectare Contingency Expenditures in Pre
and Post-reform Period 134
6.3.5 Delivery Performance Ratio of Selected
Distributaries in Pre and Post-reform Period 135
6.3.6 Comparison of Head-Tail Equity in Water
Distribution on the Selected Distributaries 136
6.4 Summary 139
7 ESTIMATION OF REGRESSION MODELS 140
7.1 Results of Wheat Regression Models 140
7.1.1 Estimation of Regression Model for Average
Gross Value Product of Wheat 142
7.1.2 Estimation of Regression Model for Average
Yield of Wheat 144
7.2 Results of Sugarcane Regression Models 145
7.2.1 Estimation of Regression Model for Average 146
vi
Gross Value Product of Sugarcane
7.2.2 Estimation of Regression Model for Average
Yield of Sugarcane 148
7.3 Results of Rice Regression Models 150
7.3.1 Estimation of Regression Model for Average
Gross Value Product of Rice 151
7.3.2 Estimation of Regression Model for Average
Yield of Rice 153
7.4 Summary 155
8 STOCHASTIC FRONTIER PRODUCTION FUNCTION
AND TECHNICAL INEFFICIENCY EFFECTS MODEL 156
8.1 Maximum Likelihood Estimates for Parameters of
Stochastic Frontier Production Function 156
8.2 Technical Inefficiency Effects Model 159
8.3 Technical Efficiencies in Crop Production 161
8.4 Summary 163
9 SUMMARY AND CONCLUSIONS 164
9.1 Summary 164
9.2 Conclusions 170
9.3 Limitations of the Study 172
9.4 Problems Faced During Study 172
9.5 Policy Recommendations 173
9.6 Future Areas of Research 175
LITERATURE CITED 177
ANNEXURES 193
vii
LIST OF TABLES
Table
No. Title Page No.
1.1 Countries or States Those Have Adopted IMT During the Past
30 Years
4
1.2 Actual Surface Water Availability in Pakistan 7
1.3 Agricultural Water Demand for Major Crops in Pakistan 8
1.4 Irrigation Network of Punjab 9
1.5 Schedule for Formation of FOs in LCC East Irrigation System of
the Punjab
21
3.1 Salient Features of the Selected Irrigation System 54
3.2 Sampled Distributaries and their Characteristics 55
3.3 Broader Category of Indicators Used at Various Levels in the
Study
63
6.1 Structure and Family Size of the Respondents in the Study Area 102
6.2 Source of Income of the Respondents in the Study Area 103
6.3 Educational Qualification of the Respondents in the Study Area. 104
6.4 Land Holding of the Respondents in the Study Area 104
6.5 Farming Experience of the Respondents in the Study Area 105
6.6 Opinion of the Farmers Regarding O&M and Quantity of
Irrigation Water
108
6.7 Opinion of the Farmers Regarding Cases of Water Theft 109
6.8 Average Yield of Major Crops Across the System 112
6.9 Average Gross Value Product of Major Crops Across the System 114
6.10 Variable Cost of Production of Wheat Crop Across the System
in Pre and Post Reform Period
117
6.11 Variable Cost of Production of Rice Crop Across the System in
Pre and Post Reform Period
119
6.12 Variable Cost of Production of Sugarcane Crop Across the
System in Pre and Post Reform Period
121
viii
6.13 Average Cost of Production of Major Crops Across the System 122
6.14 Average Gross Margin of Major Crops Across the System in Pre
and Post Reform Period
125
6.15 Ratio of Gross Margin to Cost of Production Across the System
in Pre and Post Reform Period
127
6.16 Comparison of Cropping Intensity of the Study Area in Pre and
Post Reform Period
128
6.17 Overall Comparison of Aabiana Assessment and Collection in
Pre and Post Reform Period
130
6.18 Overall Comparison of Per Hectare Operation and Maintenance
(O&M) Expenditures in Pre and Post Reform Period
132
6.19 Per Hectare Salary Expenditures in Pre and Post Reform Period 133
6.20 Per Hectare Contingency Expenditures in Pre and Post Reform
Period
134
6.21 Comparison of Delivery Performance Ratio at Head and Tail of
the Selected Distributaries in Pre and Post Reform Period
137
6.22 Comparison of Equity in Water Distribution on the Selected
Distributaries in Pre and Post Reform Period
138
7.1 Descriptive Statistics of Important Variables for Wheat Crop 141
7.2 Estimated Parameters of the Income Model for Wheat Crop 143
7.3 Estimated Parameters of the Yield Model for Wheat Crop 144
7.4 Descriptive Statistics of Important Variables for Sugarcane Crop 146
7.5 Estimated Parameters of the Income Model for Sugarcane Crop 148
7.6 Estimated Parameters of the Yield Model for Sugarcane Crop 150
7.7 Descriptive Statistics of Important Variables for Rice Crop 151
7.8 Estimated Parameters of the Income Model for Rice Crop 153
7.9 Estimated Parameters of the Yield Model for Rice Crop 154
8.1 Maximum Likelihood Estimates for Parameters of Stochastic
Frontier Production Function and Inefficiency Effects Model
157
8.2 Distribution of Technical Efficiency Estimates 162
ix
LIST OF FIGURES
Figure
No. Title Page No.
1.1 Schematic Diagram of Canal System in Punjab 11
1.2 Flow Diagram Showing the Composition of Punjab Irrigation and
Development Authority
23
3.1 Sampling Framework and Design 58
4.1 Input-Oriented Measures for Technical and Allocative Efficiency 72
4.2 Stochastic Frontier Outputs 78
6.1 Average Yield of Wheat Crop Across the System in Pre and Post
Reform Period
113
6.2 Average Yield of Sugarcane Crop Across the System in Pre and Post
Reform Period
113
6.3 Average Yield of Rice Crop Across the System in Pre and Post
Reform Period
113
6.4 Average Cost of Production Wheat Crop Across the System in Pre and
Post Reform Period
123
6.5 Average Cost of Production of Sugarcane Crop Across the System in
Pre and Post Reform Period
123
6.6 Average Cost of Production of Rice Crop Across the System in Pre
and Post Reform Period.
123
6.7 Comparison of Gross Margin of Wheat Crop Across the System in Pre
and Post Reform Period
126
6.8 Comparison of Gross Margin of Sugarcane Crop Across the System in
Pre and Post Reform Period.
126
6.9 Comparison of Gross Margin of Rice Crop Across the System in Pre
and Post Reform Period
126
6.10 Comparison of Cropping Intensity of the Study Area in Pre and Post
Reform Period.
128
x
All praises and thanks are for ALMIGHTY ALLAH The compassionate, The
merciful, The only creator of the universe, and the source of all knowledge and
wisdom Who blessed me with health, thoughts, talented teachers, co-operative
friends and opportunity to make some contribution to the already existing ocean
of knowledge. I offer my humblest thanks to the greatest social reformer and
Madina-tul-Ilm, The Holy Prophet Hazrat Muhammad (PBUH), for His humanity.
I deem it my utmost pleasure in expressing my heartiest gratitude with the
profound benedictions to Dr. Muhammad Ashfaq, Associate Professor,
Department of Agricultural Economics, University of Agriculture, Faisalabad
for providing me with strategic command at every step. I extend deep emotions
of appreciation, gratitude and indebtedness for his valuable guidance.
I also wish to express my feelings of sincerest gratitude to my Committee
member Dr. Sarfraz Hassan, Associate Professor, Department of Environment and
Resource Economics for his sincere cooperation and encouragements. I deem it
to my utmost pleasure to avail this opportunity in recording my deep feelings of
regards and sense of gratitude to Dr. Intizar Hussain, Senior Water Resources
Management Specialist, Islamic Development Bank, Jeddah, who in spite of his busiest
schedule provided substantial guidance and invaluable assistance in bringing
this dissertation to its present form.
I also feel proud to acknowledge the sincere help of Dr. M. Iqbal Zafar, Dean
Faculty of Agri Economics and Rural Sociology, for inspiring guidance during
my study period.
I don’t have words at command in acknowledging that all the credit goes to my
loving Father, Mother, Brothers, Sister and Sweet wife for their amicable
attitude and love, immense orison, mellifluous affections, inspiration, well
wishing and keen interest which hearten me to achieve success in every sphere
of life. I can never forget the innocent prayers of my sons, Ahmed Hassan,
Muhammad Taha Arif and daughter, Aleena Arif. Their prayers are the roots of my
success.
xi
My thanks are also due to the kindness and love of my Friends specially Irfan
Ahmad Baig, who always encouraged me and played a pivotal role in achieving
higher goals of life.
Cordial love and thanks to my beloved Nieces Dr. Ambreen Pervaiz, Sania Pervaiz
and Rabia Pervaiz, Aysha and Harrm whose hearts beat with golden sentiments,
whose hands always raised for my success.
I have no words of thanks for my Bhabi Farhit-un-Nisa (Late) who always wished
to see me glittering high on the sky of success during her life. May Allah rest her
soul in peace.
(MUHAMMAD ARIF RAZA)
xii
DEDICATED
TO
My Sweet and Beloved parents
And
My Loving and Caring
Family Members
xiii
ABSTRACT
Agriculture is crucial to Pakistan‘s economy and irrigation is the lifeblood of agriculture. The
irrigation system of Pakistan is the largest integrated irrigation network in the world. The state
managed surface irrigation in Punjab had not been performing well and was deteriorating day
by day due to financial, managerial and socio-political factors. Keeping in view the above
discussed problems, the World Bank proposed commercialization and privatizations of the
irrigation system as the only choice for rehabilitation. However after a series of negotiations,
the government of Pakistan agreed upon institutional reforms in water sector of the Punjab.
Consequently, in 1997, Pakistan‘s provincial assemblies passed bills to implement
institutional reforms in the country‘s irrigation sector. In the province of Punjab, institutional
reforms have been introduced in the Lower Chenab Canal (LCC) East irrigation system of the
Punjab as a pilot project through PIDA Act of 1997.
Under these reforms, management at secondary canal level (distributaries) has been handed
over to the Farmers Organizations FOs). The present study was designed to assess the
effectiveness of ongoing irrigation reforms in terms of improving water delivery, operation
and maintenance (O&M) of irrigation system, equity in water distribution and overall
management of irrigation system. It also envisaged the early effects/ impacts of irrigation
reforms on overall agricultural productivity and farm income.
A well represented sample size of 30 distributaries and 360 farm households was selected for
data collection. A multistage sampling technique was used for sample selection. The study
employed two level analysis. At first level, assessment of reforms in LCC East (Reform Area)
was made on the basis of information from the secondary sources taking into account ―Before
and After‖ reform scenario. At second level, assessment of reforms was carried out on the
basis of primary data collected at farm household level. Quantitative analysis was conducted
by making comparison of set of well established indicators developed by secondary
information at distributary level to determine the impact of irrigation reforms on water
charges (Aabiana) collection, operation and maintenance of the system, delivery performance
ratio (DPR) at head and tail of the distributaries etc. A single equation model was used to
capture the impact of irrigation reforms on farm income and productivity. Economic
xiv
Inefficiency model was also estimated to determine the negative impact of irrigation reforms
on inefficiency of the respondents.
The results of the study based on comparison of indicators from primary data showed that
there was an increase in the crop yields. On an overall basis, all the major crops (wheat,
sugarcane and rice) showed an increasing trend in yields. Wheat yield increased by 10
percent, sugarcane by 5 percent and rice by 13 percent respectively. Average gross margin of
wheat, sugarcane and rice increased by 6 percent, 38 percent and 43 percent respectively in
post reform period. The results of the study showed that cost of production of major crops
reduced after reform process. While estimating regression model, Average gross value
Product (GVP/acre) of crops (in real prices) was taken as dependent variable to capture the
effect of reform process, location of the farm along the distributary and important components
of variable cost of production. Similarly, average yield per acre of crops was taken as
dependent variable to determine the impact of reform process. The results of the regression
model for wheat, sugarcane and rice yield showed that F-Value was 7.08, 6.6 and 5.5
respectively, showing that over models were significant at less than 5 percent significance
level. For the estimation of stochastic frontier production function and inefficiency effect
model Cobb-Douglas form of production function and translog were used. The key finding of
the Inefficiency Effects Model was that the dummy for reforms had negative impact on
inefficiency effect for all the crops.
The results of the study showed that Aabiana collection increased from 42 percent to 62
percent in post reform period. The study also showed that delivery performance ratio at the
tail of the distributary increased after introduction of reform process in the province of
Punjab. It was concluded that that the institutional reforms in the irrigation sector have
positive impacts on the yield and productivity of the farmers for all the major crops. It was
also evident that the reforms also have significant impact on the farms located at the tail
clusters of the distributaries.
1
CHAPTER 1
INTRODUCTION
Water is important for human and plant life on the earth. It plays a decisive role in the
sustainable livelihoods of rural people. Approximately 40 percent of the world‘s food supply
is produced on the irrigated land (Johnson III 1995). Improvement in access to water serves as
a powerful tool to diversify livelihoods and reduce exposure for small producers. Irrigation
water creates options for extended production across the year, increases yields and outputs,
and creates employment opportunities. Increased household income may be spent locally thus
helping to stimulate the rural economy. For the last two decades, an ever-increasing number
of countries around the world have been turning over the management authority for irrigation
systems from government agencies to farmers or other non-governmental organizations. This
phenomenon is generally referred to as management transfer or devolution.
Water is precious resource. Only 2.5 percent of the world water is not salty, and of two- third
is locked up in the form of ice caps and glaciers. Due to the continuous hydrological cycle,
about two-third of remaining water is lost to evaporation while, some 20 percent of the
remaining potentially useable water is in areas too remote for human access. After deducting
all the quantities of water which can not be utilized by the human beings (for example excess
water during the monsoon or the flood water), only 0.08 percent of the total water on the
planet is actually utilized by the mankind (Lashari et al. 2003). Agriculture is the largest
consumer of water. Ever increasing population of the earth is putting more pressure on the
agriculture sector to meet the demands of the increased population, especially food
requirements. Irrigation water, the single most important input for the agriculture sector, is
even under more stress as compared to other inputs due to limited supplies. Need for
improvement in efficiency and productivity of irrigation water has become one of the key
issues for the irrigation as well of the agriculture sector. It has been observed that the state
owned irrigation systems have not been performing well and are deteriorating day by day,
especially in developing countries due to financial, managerial and socio-political factors
(Haq 1998). Literature and world experiences on irrigated agriculture have clearly indicated
2
that without integrated approach of water resources that includes irrigation, drainage and
environment, the agricultural productivity and sustainability would not be possible in the
developing countries. The linkages and coordination among all stakeholders of irrigated
agriculture is the most important institutional intervention. The irrigation and drainage sector
plays a vital role in the food supply as well as in the economy of Pakistan.
The Indus Basin Irrigation system of Pakistan is the largest contiguous irrigation system in the
world, serving in excess of 14 million hectares (Johnson III 2004). The system is fed by the
waters of the Indus River and its tributaries. It consists of three major storage reservoirs,
namely, Tarbela and Chashma on River Indus, and Mangla on River Jhelum, with a present
live-storage of about 15.4 BM3 (12.5 MAF), 19 barrages; 12 inter-river link canals and 43
independent irrigation canal commands. The total length of main canals alone is 58,500 Km.
Water courses comprise another 1,621,000 Kms (Shaikh 2004).
The Indus Basin Irrigation System of Pakistan is now facing multiple problems like
deterioration of infrastructure, high conveyance losses and inequitable water distribution both
under normal supply and shortage conditions. There has been chronic inequity with the
upstream water users receiving more water than their due share, while those in the Tail1
reaches of the canal command receiving less. The system is steadily deteriorating and
performing far below user‘s expectations; and there is a great mistrust between the irrigation
department and the users. Some of the causes of ever declining system performance are
inequity in water distribution, poor operation and maintenance (O&M) of the system, poor
water charges recovery (Aabiana), rent-seeking, political interference and weak capacities of
government institutions.
Keeping in view the above mentioned problems, the World Bank proposed that involving the
stakeholders in decision making and operation and maintenance process of the irrigation
system is the only solution for rehabilitation of the existing irrigation system. Consequently,
the government of Pakistan agreed to introduce institutional reforms in the irrigation sector of
provinces. In 1997, Pakistan‘s provincial Assemblies passed bills to implement institutional
1 Last 20 percent portion of the total length of canal, distributary or minor.
3
reforms in the country‘s irrigation sector (Nakashima 1998). In the province of Punjab, the
institutional reforms were introduced through the PIDA Act of 1997.
1.1 A Brief History of Irrigation Reforms in the World
―Until the late 1800s, the bulk of irrigation in the world was developed by users and operated
through a participatory process at the village level. These irrigation systems were developed,
operated, and maintained using local resources largely provided by the water users. Working
together, users made decisions about water allocation, established priorities for repairs and
system expansion and jointly established contributions in cash and kind to be provided by all
who received irrigation and drainage services from the system (Martin et al. 1986).
In contrast, the vast amount of irrigation and drainage development that has occurred since the
early 1900s was quite different. Most of these large-scale irrigation and drainage schemes
were developed by public agencies. Although some early development, such as that in British
India and the Western United States, that were carried out by large agri-business firms, yet
these were gradually shifted to public sources. Various development organizations and
international financial institutions became an increasingly important part of this mix.
Irrigation thus changed from being an activity under the control of local community to a
responsibility of some public organizations. Rather than becoming the responsible parties,
users became passive recipients of the services. Through the 1950s and 1960s, with massive
help from the donor agencies public irrigation development followed a model that excluded
users from active involvement in management.
By the early 1970s, however, it was becoming obvious that this model had created irrigation
systems that were difficult to operate and maintain and were open to extensive rent-seeking,
and becoming less and less sustainable (Repetto 1986). After a period of rapid expansion of
irrigated area from the 1950s to the early 1980s, many governments found it difficult to
finance the recurring costs of irrigation or to collect water charges from the farmers. Centrally
financed bureaucracies tended to lack the capacity to be effective providers of water services
to large number of small farmers. These factors led to rapid deterioration of infrastructure,
shrinkage of area irrigated, maldistribution and wastage of water (Vermillion and Sagardoy
1999). At this stage, a number of irrigation specialists articulated the need for all new
4
paradigm for irrigation development as they recognized that sustainable irrigation systems
require active participation of the users in order to be properly operated and maintained
(Coward and Jr 1987).
Since the mid 1980s, there has been an upsurge in efforts by governments around the world to
transfer management for irrigation systems from government agencies to farmer organizations
or other non-governmental entities. This has occurred more or less in developed and
developing countries. Generally, governments hope that Irrigation Management Transfer
(IMT) will reduce the cost burden of irrigation on the government and will increase
productivity and profitability of irrigated agriculture enough to compensate for any increase in
the cost of irrigation to the farmers.‖
Among the pioneers having experience in irrigation management transfer (IMT) USA,
Mexico, Australia and Turkey are few good examples. Countries, such as Chile, Mexico and
China, are well along in this process. Other countries, such as Indonesia and the Philippines,
and some States in India have embarked on transfer programmes but appear to be bogged
down in problems of implementation. Some countries have transferred small scale systems
and now are considering transferring large scale systems (Vermillion and Sagardoy 1999).
Table 1.1 shows list of countries that have adopted irrigation management policies over the
last 30 years.
Table 1.1: Countries or States Those Have Adopted IMT During the Past 30 Years
Latin America South, South East and
East Asia
Africa& Near East Europe &Central Asia
Brazil, Chile,
Colombia,Dominican
Republic, Ecuador, El
Salvador, Guatemala,
Peru, Mexico
Bangladesh, China,
India, Indonesia, Laos,
Nepal, Pakistan,
Philippines, Sri Lanka
Vietnam
Ethiopia, Ghana,
Jordan, Madagascar,
Mali, Mauritania,
Morocco, Niger,
Nigeria, Senegal,
Somalia, South
Africa, Sudan,
Turkey, Zimbabwe
Albania, Armenia,
Bulgaria, Cyprus,
Georgia,
Kazakhstan,
Macedonia,
Moldova, Romania
Source: Vermillion and Sagardoy 1999
Overtime, irrigated agriculture has increased its importance in the world as a source of food
security, higher farm incomes, and increase in welfare of both rural and urban populations.
5
The development of irrigation in 20th
century played an important role in generating food
surplus that have led to economic development in Asia. Over 60 percent of the world‘s
irrigation is in Asia and since 1965 the irrigated area has almost doubled (Barker 2002). The
world has moved beyond the period when food security was the major goal and construction
of large dams and surface irrigation systems was seen as the major investment needed to
achieve that goal. It is now a challenge to produce more food with less water, to enhance
livelihood and alleviate poverty in the rural areas, and to manage water to protect the
environment and human health. This calls for a new approach to water management.
1.2 Agriculture and Economy of Pakistan
Pakistan is, basically an agricultural country. Agriculture is the backbone of Pakistan‘s
economy. Agriculture is not only the main stay of the populace, directly or indirectly, for
seeking food, clothing employment and perhaps everything, but also viewed as a dominant
way of life. Our culture, habits and attitudes derive their roots, inter alias, from the agriculture
being practiced in this part of world. Therefore, the development of agriculture is synonymous
to the development of the people as well as the country. The importance of water for Pakistan
can not be under-estimated, particularly for irrigated agriculture in the country. In Pakistan,
irrigated agriculture covers 16.2 million hectare (74 percent) out of the total cultivated area of
22 million hectare. Irrigated agriculture uses 97 percent of the available water and provides
over 90 percent of agricultural produce (Shaikh 2004). Agriculture accounts for 20.9 percent
of GDP, and employs 43.4 percent of labor force. It supplies most of the country‘s needed
food grains and also is a source of raw materials for major domestic industries. As such,
agriculture is at the center of the national economic policies and has been designated by the
Government as the engine of national economic growth and poverty reduction. The major
crops grown are cotton, rice and sugarcane in the rainy season and wheat in the dry season.
Cotton alone accounts for 8.6 percent of the value added in agriculture and about 1.8 percent
to GDP (GOP 2007). The former crops are produced in the irrigated areas and the latter is
produced in both irrigated and non-irrigated areas. In the dry season fodder crops are
produced in the irrigated areas because of high importance of livestock sector in Pakistan
(Nakashima 1998). The health of the agricultural sector also has important implications for
poverty reduction and private sector development.
6
There are two principal crop seasons in Pakistan, namely the Kharief, the sowing season of
which begins in April-June and harvesting during October-December; and the Rabi, which
begins in October-December and ends in April-May. Rice, sugarcane, cotton and maize are
major Kharief crops while wheat, gram, lentil tobacco, rapeseed, barley and mustard are Rabi
crops. Major crops, such as, wheat, rice, cotton and sugarcane account for 88.7 percent of the
value added in the major crops. The value added in major crops accounts for 36.3 percent of
the value added in overall agriculture. Thus, the four major crops (wheat, rice, cotton, and
sugarcane), on average, contribute 32.2 percent to the value added in overall agriculture. The
minor crops account for 11.7 percent of the value added in overall agriculture (GOP 2007).
In Pakistan, average rainfall is less than 240 mm a year. In the cultivable plains, rainfall
ranges from about 500 mm a year along the Punjab border with India (which receives some
rainfall from the summer monsoon) to only 100 mm a year in the western parts of Pakistan.
The low precipitation level mean that rain-fed, or barani, agriculture is not possible on a large
scale in Pakistan. Throughout history people have adapted to the low and poorly distributed
rainfall by either living along river banks or by careful management of local water resources
(World Bank 2005). The balance between population and available water already makes
Pakistan one of the most water-stressed countries of the world and with rapid population
growth it will soon enter a condition of absolute water scarcity (World Bank 1994). The
irrigated agriculture of Pakistan mainly depends on Indus River System and its tributaries.
The annual flow of Indus River is 143 MAF out of which 103 MAF is diverted into different
canal commands. Being semi-arid climate of the country, having an annual rainfall of 240
mm, the 90 percent of the irrigated agriculture is being carried out in Indus Plains. The 80
percent flow of the Indus River is generated during monsoon i.e. from June to August, which
necessitates effective water management for sustainability of irrigated agriculture (Qureshi
and Haq 2006). Pakistan‘s agricultural output is closely linked to the supply of irrigation
water. Actual surface water availability in Pakistan against the normal surface water
availability at canal Heads is shown in Table 1.2.
7
Table 1.2: Actual Surface Water Availability in Pakistan
Period Kharief
(MAF)
Percentage
increase/decrease
over the average
Rabi
(MAF)
Percentage
increase/decrease
over the average
Total
(MAF)
2001-02 54.7 -18.4 18.4 -49.5 73.1
2002-03 62.8 -6.4 25 -31.3 87.8
2003-04 65.9 -1.8 31.5 -13.5 97.4
2004-05 59.1 -11.9 23.1 -36.5 82.2
2005-06 70.8 5.5 30.1 -17.3 100.9
2006-07 63.1 -6 31.2 -14.3 94.3
Average system usage
67.1 _ 36.4 _ 103.5
Source: GOP 2007
Above Table 1.2 shows that during the fiscal year of 2006-07, the availability of water for
Kharief 2006 for major crops such as rice, sugarcane and cotton has been 6.0 percent less than
that for the normal supplies and 10.8 percent less than last year‘s Kharief. The water
availability during Rabi season (for major crops such as wheat) was estimated at 31.2 MAF,
which was 14.3 percent less than the normal availability. Thus it is clear that from the above
Table that water availability during the last many years have gone down.
Large part of Pakistan has good soils, abundant sunshine and hardworking farmers. And yet
crop yields, both per hectare and per cubic meter of water, are much lower than international
benchmarks and much lower than in neighboring areas of India. The quality of water service
plays an important role in enhancing productivity through equity and reliability of surface
water.
Pakistan is required to double its annual food production every 15 years in order to maintain
its status quo in meeting requirements of food. This target, on the surface, may not look so
demanding, as the country is bestowed with enough fertile and productive lands and sufficient
freshwater-resources. Despite the availability of these basic resources, unfortunately the
country has to import large quantities of food commodities every year. With the current
population of about 151.55 million people which are growing at the rate of almost 2.6 percent
per annum (GOP 2007), the country would have to feed 120 million additional mouths by the
year 2025 (Kahlown 2005). In such a situation, it is inevitable to keep a balance between
8
production of crops and crop water requirements. Table 1.3 shows the production and water-
requirements of some major crops needed to maintain self-sufficiency in food grains.
Table 1.3: Agricultural Water Demand for Major Crops in Pakistan
Crops Agricultural Water Demand (MAF)
1990 2000 2025
Wheat 26.27 28.8 56.91
Rice 18.78 22.24 56.91
Cotton 13.68 15.71 16.68
Sugarcane 11.35 13.41 19.35
Other Crops 28.93 30.59 46.74
Total with losses @70
percent
168.32 188.28 261.14
Source: GOP 2000
1.3 Irrigation Sector in Punjab
Punjab is the largest province of Pakistan, located in the middle of the country with fertile
irrigated lands. All of its total irrigated area lies in the Indus basin, which is one of the largest
irrigation systems in the world. Irrigation system of Punjab consists of major part of Indus
Basin Irrigation System (PIDA 2005). This system was built up almost a century ago on run
off river basis. This system is considered as a life line for sustainable agriculture in Punjab
which feeds almost whole the country. The irrigation net work of Punjab is a part of Indus
Basin Irrigation System of Pakistan designed for initial cropping intensity ranging from 60 to
80 percent (PIDA 2005). The Punjab irrigation net work comprises of irrigation canals,
drains, tube-wells, small dams and flood protection infrastructures. There are 14 main
barrages on five rivers supplying 120,000 cusecs of water to the fields with 110,000 cusecs
capacity of inter link canals. The colossal net work of over 23000 miles of irrigation channels
provides irrigation facilities to about 8.41 million hectares (PIDA 2005).
Irrigation being a provincial subject, Irrigation Department has historically been responsible
for all water sector activities at provincial level, including administration, planning,
development, operation and maintenance of irrigation and drainage, flood control and
reclamation work. The Irrigation and Power Department is a government body, Headed by the
Secretary to the government of the Punjab, Irrigation and Power Department with Chief
9
Engineers, Superintending Engineers and Executive Engineers to work in the field offices
along with other staff to provide irrigation facilities to the farmers. Present status of irrigation
net work in Punjab is shown in Table 1.4.
Table 1.4: Irrigation Network of Punjab
Head Works/ Barrages
14 No.
Main Canal System
21No.
Length of Main Canals & Branches
6,389 Km.
Distributary & Minors
2,794 Km.
Total off-taking Capacity
120,000 Cfs.
Outlets
50,000 Nos.
GCA/ CCA
23.35/ 20.78 Mac.
Annual Permissible Irrigation
13.96 Mac.
Design Intensity
67 percent
Actual Irrigation
25.50 Mac.
Actual Irrigation Intensity
122 percent
Source: GOP 2005
The irrigation network of the Punjab was initially designed for 67 percent cropping intensity.
But presently actual irrigation intensity has increased to 122 percent, showing that the system
is already overburdened.
1.4 Canal Irrigation System of Punjab
The main objective of any effective canal system is to provide ensured water supply to the
farmers throughout the year without any interruption. As water is scarce resource in Pakistan,
hence the objective was to allocate this resource over a large geographic area on an equitable
basis. The desired pattern of water allocation was to be achieved through design of systems‘
10
structure. The canal irrigation system of Punjab is classified into three distribution level.
These are: main canal level, distributary level and watercourse level (PIDA, 2005).
1.4.1 Main Canal Level
Main canals are the most crucial constituent of the irrigation system for controlled diversion
of irrigation supplies to sustain irrigated agriculture in Punjab. Main canals originate from the
river and are the main supply line for branch canals. In Punjab, there are 21 main canals with
total length of 6389 km, which support all the irrigated area of the province. The effective and
efficient operation and maintenance of these canals is the responsibility of Punjab irrigation
department.
1.4.2 Distributary Level
The distributaries off take from the main canal system. There is a complex network of
distributaries which supply water directly to outlets. The outlets are designed to take water
automatically from the distributary. Irrigation and Power Department of the Punjab has been
responsible for maintaining irrigation water flow in the distributaries.
1.4.3 Watercourse Level
This is tertiary level which directly supplies water to the farmers‘ fields. It is based on the
rotational operation plan, which is controlled on hourly basis to irrigate each farmland. From
the outlets water is directly supplied to watercourses. Farmers are responsible for operation
and maintenance of watercourses at this level. The structure of irrigation network of Punjab is
depicted from the Figure 1.1.
11
Figure.1.1: Schematic Diagram of Canal System in Punjab
Source: GOP 2005
Figure 1.1 shows the structure of irrigation network from Head works to the farmer‘s field.
The major responsibility for irrigation system management rests with the provincial irrigation
department (PID), and some of its elements are with Provincial Agriculture departments. PID
undertakes some construction works, but primarily attend to the operation and maintenance
(O&M) of irrigation facilities, extending from barrages and main canals to outlets, upkeep and
maintenance of drainage and flood works, assessment of water charges and resolution of
conflicts among water users (Haq 1998).
_________________________
Some text in section 1.5 has been derived and reproduced from ―Managing Irrigation for Environmentally
Sustainable Agriculture in Pakistan‖ by Asrar-Ul-Haq (1998).
12
1.5 Objectives of Irrigation System in Punjab
The Irrigation system of the Punjab has the following two kinds of objectives.
1.5.1 Design Stage Objectives
To improve control and command for the acquisition and distribution of
irrigation water.
Optimal allocation and utilization of scarce water resources.
Bringing maximum area under cultivation to benefit the rural population with
available irrigation water.
Partial irrigation with restricted cropping intensities.
Operation of the system with minimum human intervention.
Equitable and proportional distribution of available irrigation supplies.
1.5.2 Operational Objectives
Effective and efficient management of irrigation and drainage infrastructure.
Equitable distribution of available canal supplies at Head, Middle and Tail end
reaches.
Control of illegal water abstractions.
Water resources development.
Control of water logging and salinity.
Revenue generation through efficient assessment of water fees.
Control of environmental degradation of land and water resources.
Resolution of conflicts related to the mutual rights of the share holders.
13
The irrigation performance needs to be reviewed in the context of system design objectives,
operational constraints, institutional systems and the broader socio-economic framework. The
various studies (World Bank 1994, Haq and Shahid 1997, Nakashima 1998, Latif and Pomee
2003) indicated that Pakistan‘s extensive irrigation system has progressively deteriorated
because of inadequate maintenance funding, overstressing of channels to meet an escalating
water demand, and a phenomenal increase in the uses of canal banks by the human, animal
and vehicular traffic. The increased trespassing has been triggered by rapid population
growth, farm mechanization, changing social order, and weakening controls. The system
deterioration is characterized by weak canal banks, eroded brim, channel cuts and breaches,
frequent sedimentation of distributaries and minors and dilapidated condition of canal
structures (Haq 1998). It is, therefore, obvious that the Punjab Irrigation Department (PID)
remained unable to meet the operational objectives.
1.6 Issues of Irrigation Management
Pakistan has significant natural water resources, but they are inadequate for crop production
on the available land. River flows are highly seasonal. Roughly 85 percent of annual flows are
in the Kharief (summer) season and only 15 percent in the Rabi (winter) season. Moreover,
due to inadequate water availability in winter and at the beginning and end of the summer,
cropping intensity is exceptionally low. The stagnant crop yields and increase in the country‘s
population demand enhancement of agricultural production in the irrigated areas. The
agriculture in Pakistan is dependent on irrigation. The system is performing poorly (World
Bank 1994a). The deterioration of the irrigation system is considered the main cause of
stagnant agriculture (Vermillion et al. 1997).The irrigation system of the Punjab is beset with
large number of problems. These were:
1.6.1 Low Irrigation and Water Use Efficiencies
The overall efficiency is the product of conveyance losses, distribution losses and the
application losses. The overall efficiency of Pakistan‘s irrigation system is estimated to range
between 35-40 percent of water from canal Head to the root zone (World Bank 1994). It
implies that for every 100 units of water diverted at the canal Head, only 40 units are
14
available to the root zone. In practical terms, this means that much surface water is currently
lost enroot-water that could be profitably used by farmers. The Indus irrigation system, which
is based on gravity flow, has low use-efficiency. Moreover, it is supply based, and so unable
to accommodate changing water demands during the crop season. Inefficient water delivery
and water use also mean that, in reality, water does not reach users toward the Tail end of the
system.
1.6.2 Poor Aabiana Collection (Water Charges)
Irrigation fees had been sufficient to cover operation and maintenance (O&M) costs until the
irrigation sector started to deteriorate in the 1970s. Due to weakened discipline, the collection
of irrigation fees from the farmers declined, and revenues fell short of government O&M
expenditures. The gap between recoveries and expenditures through water fees was 44 percent
in 1992, which was high and increasing (World Bank, 1994). The current studies also showed
that cost recovery in Punjab before the irrigation management transfer was 44 percent only
(Latif and Pomee 2003).
1.6.3 Inequitable Distribution of Irrigating Water
Water distribution, contrary to the system‘s objective, is not equitable (World Bank 1994).
Equity in water allocation and distribution has many dimensions and levels; inter and intra
canal equity, inter and intra distributary equity, and inter and intra watercourse equity.
Inequity in irrigation water distribution is the most serious problem for the farmers. It has
been observed that inequity in water distribution increases with the increasing length of
distributary. There are three categories of farmers receiving canal water. The categories are;
1) farmers getting more water than their due rights, 2) farmers getting the right share of water,
and 3) farmers suffering from scarcity of water. The categories 2 and 3 are un-satisfied
farmers since the basic system is designed for an inadequate supply of water and even the
right share is not sufficient. According to an official source, 20 percent of the farmers fall in
category 2 and 3 are from the Punjab province. Out of this group, 10 percent are severely hit
farmers, receiving negligible or no water (Nakashima 1998).
15
1.6.4 Inadequate Maintenance of the System
The operation and maintenance (O&M) of the entire irrigation network is one of the major
management issues of the water sector, which starts from the rim station to the farmer‘s fields.
Maintenance of distributaries include desilting, restoration of distributary banks and secure
hoes and rebuilding of regulators and bridges. Such works are carried out by contract unless
they are very small. The extent of canal maintenance is thus determined by the amount of
non-development budget and what remains after paying for the establishment.
In 1996, collapses of two major structures, the out-fall structure of Balloki-Suleimanki-I Link
and regulator-cum- bridge on Marala-Ravi Link, have raised serious concerns about the state
of health of the irrigation network in the province (Haq 1998). The Government has not even
adequately met the requirements of an administered system. It has failed to make budgetary
provisions for operations and maintenance. Moreover, the public body responsible for
irrigation maintenance is separate from the agency responsible for revenue collection. In the
past, administrative discipline was adequate but it has now broken down and the cost of
irrigation maintenance has vastly increased. The issue has become increasingly severe over
the last many years, and is the outcome of a host of factors. Increasing water demand,
deferred maintenance, siltation of distributary prisms, excessive withdrawal by outlets and
illegal water extractions all contribute towards the increasing inequity in the system. This has
eroded the confidence of the Tail users in the integrity of the system.
1.6.5 Poor Irrigation Infrastructure
Most of the water infrastructure is in poor condition. Pakistan is extremely dependent on its
water infrastructure, and it has invested in it massively. Due to a combination of factors such
as age, time neglecting attitude of the department towards repair and maintenance of existing
infrastructure, much of the infrastructure is crumbling. This is true even for some of the major
barrages, which serve millions of hectares and where failure would be catastrophic. There is
no modern Asset Management Plan for any of the major infrastructure (World Bank 2005).
16
1.6.6 Illegal Diversion from Distributaries
There have been increasing incidences of tampering of outlets and other regulation structures,
combined with cuts and breaches at the Head and the Middle of the distributary, which caused
serious distortions in the established operational patterns, thereby impinging adversely on the
system performance. It was found that the farmers at the Tail reaches were badly effecting
from such kind of breach of irrigation water.
1.6.7 Inadequate Farmer’s Participation in Irrigation Management
The performance of the state managed irrigation systems, including the huge integrated Indus
Basin Irrigation System of Pakistan, has been on decline, and is an equal cause of concern for
policy makers, managers and the users. One main reason for this decline is lack of
involvement of users in the management of the system (Mirza et al. 2000). The desired level
and frequency of contact between the irrigation agency staff and the farmers has, however,
diminished overtime. Resultantly, the water theft and water use of canal roads is on the
increase. There has been a growing recognition that any worthwhile improvement may not be
possible without implementing effective programmes for farmer participation in the
prevailing socio-economic environment (Haq 1998).
1.6.8 Corruption and Rent Seeking Behavior of the Officials
Irrigation water is scarce in Pakistan and is distributed to the farmers through administrative
rationing. In response to growing water scarcity, farmers increasingly engage in informal
negotiations and extralegal transactions with irrigation agency officials in order to obtain
more water than their legal quota (Rinaudo 2002). Hence such kind of negotiations may lead
to appropriation of extra canal water by the farmers favorably located at Head end reaches of
canal, at the cost of farmers located at the Tail end reaches of canal.
1.7 Need for Institutional Reforms in Irrigation Sector
The poor functioning of the irrigation system in Pakistan has been a source of concern since
the 1960s and since then it has been the subject of considerable external assistance and
internal policy reforms (Latif and Pomee 2003). However, the need for improving irrigation
17
management has become a major priority on the agenda of most national and international
agencies in the recent past. This was triggered by the declining irrigation performance despite
sizeable investments in the rehabilitation of irrigation infrastructure. Thus learning from the
experience of other nations of the world, it was recognized that the existing irrigation
management organization be changed by shifting the responsibility of management from
government managed agency (PID) to the farmers. Considering the situation, the Government
has introduced institutional reforms in the irrigation sector of the Punjab. One important
aspect of the reforms is irrigation management transfer (IMT) by user‘s participation in the
management of the system called ―Participatory Irrigation Management‖ (PIM).
1.7.1 Irrigation Management Transfer (IMT)
The term ―Irrigation Management Transfer‖ means the relocation of responsibility and
authority for irrigation management from government agencies to non-government
organizations, such as water users associations. It may include all or partial transfer of
management functions. It may be implemented at sub-system levels, such as distributary canal
commands, or for entire irrigation systems or tube-well commands (Vermillion and Sagardoy
1999).
1.7.2 Participatory Irrigation Management (PIM)
The term ―Participatory Irrigation Management‖ normally refers to involvement of water
users in irrigation management along with the government (Vermillion 1999). It is assumed
that the transfer of authority from the government to farmers would result in better
management of irrigation system in terms of dispute resolution, equity in water distribution
and overall management of the system as farmers understand the irrigation problems at farm
level much better than the government staff.
1.8 PIM Model for Punjab
The irrigated agriculture is facing organizational changes worldwide. There is growing
recognition that irrigation water management is a service provided to customers with better
results when operated by decentralized organizations (Lashari 2006). On cognizant of the
problems in irrigated agriculture and water management in the Province, the Government of
18
the Punjab decided to adopt the institutional reforms in the irrigation sector. Hence, in 1997,
the Punjab Provincial Assembly passed the ―Punjab Irrigation and Drainage Act‖. The Punjab
Irrigation and Drainage Authority (PIDA) have been set up at provincial level with the
representation of the farmers and the government representatives.
The main objectives of reforms initiatives as brought out in PIDA Act are as follows.
Implement the strategy of the government of the Punjab for streamlining the Irrigation
and Drainage system.
To replace the existing administrative organization and procedures with more
responsive, efficient and transparent manners.
To achieve economical and effective O&M of the irrigation, drainage and flood
control system.
To make the irrigation and drainage network sustainable on a long term basis; and
Introduce the participation of beneficiaries in the O&M of the irrigation and drainage
systems.
However, the principal objective of reforms in irrigation sector of the Punjab Province is to
reverse the deteriorating performance of its irrigation system and the consequent stagnating
productivity of irrigated agriculture in the Indus Basin. Under the reform model, new
institutions have been designed and implemented on pilot testing basis in Punjab. This is to be
accomplished primarily through two institutional policy initiatives.
One is the restructuring and decentralization of Punjab irrigation department (PID)
into autonomous Punjab Irrigation and Drainage Authorities (PIDA) and Area Water
Boards (AWB).
________________________
Some text in section 1.9 has been derived and reproduced from ―Reforms in Irrigation Sector: Vision,
Implementation, Achievements.‖ Report published by PIDA (2006).
19
The other is to include local irrigation communities in the management of the
irrigation system by developing operational and maintenance as well as fiscal
responsibilities for secondary canal channels through independent, self-sustaining
Farmer Organizations (FO). Thus the institutional frame consists of three entities:
1. Punjab Irrigation and Drainage Authority (PIDA)
2. Area Water Board (AWB)
3. Farmers Organizations (FOs)
1.9 Description and Functions of PIDA, AWB and FOs
The formation and functions of Punjab Irrigation Development Authority (PIDA), Area Water
Board (AWB) and former organizations is given below.
1.9.1 Punjab Irrigation and Drainage Authority (PIDA)
PIDA is an autonomous body which performs the following main functions:
a. To carry out all the functions of Irrigation Wing of the Punjab Irrigation
Department (PID) with independent revenue collection and purchasing authority.
b. Responsible for policy formulation, legal enactment and supervision of the overall
management of Irrigation and Drainage System in the province.
c. To plan, designs construct, operate and maintain the Irrigation and Drainage and
flood control infrastructure located within the territorial jurisdiction.
d. To take measures for reducing O&M expenditures and improving maintenance
planning.
e. To make the Authority financially self-sustaining with regard to O&M cost of
canal irrigation and drainage within a period of 7-10 years.
20
1.9.2 Area Water Board (AWB)
Under PIDA, Area Water Board (AWB) is financially self-sufficient entity at the canal
command level which performs the following functions.
a) Responsible for the irrigation and drainage management of the main canal system,
including bulk water supplies to the Head of the distributaries.
b) Review and monitor the operation and maintenance work plan of the canal.
c) Participate in the operation, implementation and regulation of the rotational
programmed of water distribution in the Area Water Board.
d) Monitor the operation of irrigation systems in the area.
e) Assist the Authority and the government in the formation, promotion and
development of Farmers Organizations
f) Monitor the working of Farmers Organizations
g) Responsible for the management of the irrigation system from barrages to the
distributary Heads, drainage and flood control structures within its territorial
jurisdiction.
1.9.3 Farmers Organizations (FOs)
Under the Area Water Boards, Farmers Organizations have been formed at distributary level.
The overall management of the distributaries has been transferred to these FOs. The FO is the
basic management unit responsible to operate and manage the irrigation and drainage
infrastructure within its jurisdiction.
1.10 Schedule for Formation of FOs
In the Lower Chenab Canal East (LCC East) command area, 85 FOs have been formed having
a total command area of 1564.5 acres. Management transfer to these 85 FOs in pilot Area
Water Board (AWB) was done in three phases of transfer to 20, 49 and 16 FOs respectively
21
during the year 2005. As a first step towards irrigation management transfer in LCC (East), 20
FOs were formed in March 2005 and IMT was transferred to them. The second and third
group of FOs were completed in June and December 2005 respectively. The detail of
formation of FOs is given in Table 1.5 below.
Table1.5: Schedule for Formation of FOs in LCC (East) Irrigation System of the
Punjab
Group of FOs No. of FOs CCA(Acres) Dated for IMT Status
First Group 20 545552 08-03-2005 Completed
Second Group 49 612924 30-06-2005 Completed
Third Group 16 405996 08-12-2005 Completed
Total 85 1564472
Source: PIDA 2005
FOs in general, are performing the following functions.
a) To obtain irrigation water supplies from the main or branch canal at its Head regulator.
b) To manage, operate and maintain the irrigation infrastructure of the channels including
any hydraulic structure according to the approved design.
c) To supply the irrigation water equitably and efficiently to the farmers.
d) To access the water charges and other irrigation related charges to be collected from
the canal water users.
To collect the water charges, fees and other dues from the farmers.
e) To deposit the collected amount of water charges with the Authority after retaining its
share in the collected amount, as agreed with the Authority.
f) To settle water disputes relating to the farmers or other water users of the area.
1.11 Legal Framework and Composition of PIDA
For implementation the reform initiatives, a legal framework has been evolved by the PIDA
which is based on the participation of the farmers at all levels of irrigation management that is
at provincial level, canal command level and at distributary level. This frame work legitimizes
the reforms process and stipulates the conditions for establishing Farmers Organizations and
22
Area Water Boards through Rules and Regulations under PIDA Act. The detail of the legal
frame work is as under:
The Punjab Irrigation and Drainage Authority Act 1997.
The Area Water Board (Rules) 2005.
Farmers Organizations (Rules) 1999, replaced with the new Rules, 2005.
FOs (Election) Regulation, 1999.
FOs (Registration) Regulation, 1999.
FOs (Financial) Regulation 2000.
FOs (Conduct of Business) Regulations 2000.
Irrigation Management Transfer Agreement between FO and AWB/PIDA.
Under this legal framework the existing management of irrigation system has been converted
into multi-tier system for management of irrigation infrastructure.
23
Punjab Irrigation Development Authority (PIDA)
(At Provincial Level)
Chairman
(Minister for Irrigation, Punjab)
Farmer Members: 6
Non-Farmer Members: 5
Chairman P&D Board
Sectary, Irrigation & Power Deptt.
Secretary, Agri. Deptt.
Sectary, Finance Deptt.
Managing Director PIDA
Chairman
(Elected Out of Farmer Members)
Farmer Members: 10
(Elected out of Farmer Organizations):
Non Farmer Members: 9
(Representative of Allied Govt. Deptt.
and Technical Experts
Farmer Organizations (FOs)
(At Distributary Level)
Khal Punchayat
(At Water Course Level)
Chairman: 1
Members: 4
General Body
Consists of Chairmen of
respective Khal
Punchayats
Management Committee
(Elected by General Body)
President: 1
Vice President: 1
Secretary: 1
Treasure: 1
Executive Members:5
(Three from Tail reaches)
Figure 1.2: Flow Diagram Showing the Composition of Punjab Irrigation and
Development Authority (PIDA)
Source: Adapted from PIDA 2005
Area Water Board (AWB)
At Canal Command Level
24
The process of Institutional Reforms commences with community development at village
level to make aware of the farming community about Participatory Irrigation Management
(PIM) initiatives and to organize them for establishment of Farmers Organization. Such
organizations have also been formed at tertiary level i.e. watercourses and are called water
user‘s associations. Thus our farmer community is already familiar with the concept of
community development.
1.12 Need for the Study
As mentioned earlier, the institutional reforms have been introduced in the Punjab Irrigation
Sector through the PIDA act of 1997 and this process of management transformation is
scheduled to be completed by the year 2011 in all Punjab. LCC (East) system of the Punjab
Irrigation is selected as a pilot project for the implementation of the reform process.
Government is investing huge amount for the amelioration of irrigation system. While in-
depth assessment of impacts of these management changes is yet to come, there are
indications from claims made so far that such transformation has brought many benefits
including improved management, lower management costs, improved O&M of the system,
improved water delivery, lower water thefts, reduced conflicts on water and the empowerment
of farmers/beneficiaries that has multiplier effects in community building and quality of life.
However, on the other hand, there have also been concerns on the potential negative effects of
new management institutions especially for small poor farmers. The results of this study will
serve as a role model for implementation and expansion of reforms to other systems in Punjab
and Pakistan.
This study will also provide the researchers/research institutions a very good footing ground
for their future research as this would be the very first quantitative analysis of highly
important relationships between water charges, O&M of the system with water use efficiency
and Head-Tail equity in the scenario of newly designed and implemented water sector
reforms.
25
1.13 Objectives of the Study
The specific objectives of the study were:
1- To assess the effectiveness of ongoing irrigation reforms in terms of improving water
delivery, operation and maintenance (O&M) of irrigation system, equity in water
distribution and overall management of irrigation system.
2- To analyze the early effects/ impacts of PIM reforms on overall agricultural
productivity and farm income.
3- To examine the institutional and financial sustainability of newly created institution
under PIM reforms.
4- To suggest the policy recommendations and guidelines for improvement in PIM
reforms for enhancing their effectiveness, sustainability and overall benefit to society.
1.14 Summary
Agriculture continues to play an important role in the economy of Pakistan. Water is crucial
for our agrarian economy of because overwhelming majority of population is directly or
indirectly dependent on agriculture as a source of livelihood. In addition to it, agricultural
produce is the economic foundation for foreign exchange earnings, making water all the more
important. The existence of gigantic irrigation system and vast networks of irrigation channels
alone, do not necessarily mean that a high level of agricultural productivity is ensured to help
poverty alleviation. The higher level of agricultural productivity, which also is
environmentally sustainable, has many other important ingredients that need to be considered.
Among these, the most important one is reliable and equitable supply of irrigation water to the
farmers in genera, and Tail-enders in particular. Past research in Pakistan shows that a low
level of agricultural productivity is associated with low performance and poor management of
the irrigation system (Mirza et al. 2000). The poor performance of the irrigation system
results in skewed and unreliable water supplies associated with many other problems. This
problem invited the attention of the government to introduce reforms in irrigation sector of
Punjab province consequently, management was transferred to the farmers under the PIDA
Act, 1997.
26
CHAPTER 2
REVIEW OF LITERATURE
The present study is an attempt to measure the performance of the newly created institution
(Punjab Irrigation and Drainage Authority) in the irrigation sector of the Punjab, Pakistan.
The study in hand is the first effort of its kind based on the primary as well as the secondary
data. So far, in Pakistan, very few researchers have made an attempt to directly probe in to the
problem that is why there is a little evidence of comparable results and no empirical literature
directly related to impact assessment of irrigation reforms is available. However, in
international scenario, many studies were conducted to evaluate the performance of Irrigation
Management Transfer (IMT). This chapter is divided in to two sections. Section 2.1 contains
review of irrigation reforms from outside Pakistan and section 2.2 studies from Pakistan.
2.1 Selected Studies from Outside Pakistan
Danial et al. (1980) indicated that the water requirement for enhancing agricultural
productivity could be better achieved at least through five measures. These measures
included: 1) Rehabilitation of existing irrigation projects in terms of modifying the
distribution net work. 2) More intensive operation and maintenance of irrigation
infrastructure. 3) More careful planning of cropping patterns. 4) Greater care in allocation
and scheduling of water both among and within systems. 5) Greater enforcement of irrigation
reforms, rules and regulations in the system.
World Bank (1994) pointed out many problems the irrigation system of Pakistan is
facing. Such problems included, water logging and salinity, over-exploitation of fresh
groundwater, low efficiency in delivery and use, inequitable water distribution, unreliable
water delivery, and insufficient cost recovery. The study also pointed out that due to age,
overuse, and poor maintenance, the efficiency of delivery of the canal system was low,
ranging from 35-40 percent from canal Head to the root zone. It was also observed that,
unless the Pakistan government changes its approach, no future strategy for irrigation and
drainage would succeed. The long-term option for the government would be to define
27
individual water property rights, which were necessary to ensure equity in water distribution.
This would address the problems of Tail-enders, on the one hand, and relieving pressure on
ground water resources, on the other.
Johnson III (1995) studied the process of Irrigation Management Transfer (IMT) in
Indonesia, Colombia, New Zealand and Nigeria. He found that in countries where
governments have had the political will to increase water fees to close to the real O&M cost,
the process of irrigation transfer was smoother. This reflected the fact that the water users
were encouraged to take over management responsibilities in order to reduce water costs. An
equally important inducement for water users to accept additional management responsibility
was better and more dependable delivery services from irrigation agencies.
Turral (1995) discussed responses to the under-performance of irrigated agriculture,
highlighting the changing relationships between the state and water users in the operation and
maintenance of publicly-funded irrigation schemes. The study begun with a summary of the
reasons for and responses to under-performance in the irrigation sector and then outline the
institutional and economic background that favoured local cooperation and coordination in
irrigation management. The focus of the study was on management transfer and privatization
of irrigation, with reference to the broader problems of inter-sectoral water allocation and the
accompanying transformation of the role of state agencies from implementation to service
provision.
Biswas (1996) suggested that water was likely to be one of the most critical resource
issues of the developing world in the early part of the 21st century. He also suggested that a
balanced and sustainable approach to water development was mandatory if the adverse
impacts of the impending water crisis were to be avoided. He was of the view that the issue of
water had been basically ignored in the international agenda in the recent past years. The
perspectives of the North and the South differ on water in certain fundamental ways. It was
examined that the global water requirements were increased almost ten-fold during the 20th
century. The first and the foremost reason was over population, which was expected to be
double to about 10.64 billion by the year 2050. The second reason was increasing water
requirement, which was basically ignored by the water planners in all developing countries.
28
He suggested that it was essential that both the developing and the developed nations should
make a concerted attempt to put water higher up in the international political agenda.
Dick (1997) examined trends in the irrigation policies towards farmer‘s participation
in irrigation management over the past 20 years. Special attention was paid to experiences of
induced participation and management transfer programs in Philippines, Sri Lanka, Pakistan,
Senegal, Columbia Basin USA, and Mexico. This paper provided key lessons related to the
value of social organizers as catalysts, the role of the irrigation agency as partner and the
enabling conditions for farmer‘s participation. As level of income and infrastructure rose,
more formal organizations that enabled farmers to deal with bank accounts, service contracts,
water rights, water markets, and advanced technology in irrigation systems were being
expected. It was also found that the impact of participation on irrigation performance needs to
be evaluated not just in terms of reductions in government costs, but also in terms of
improvement in physical infrastructures and farmers‘ control over water.
Kloezen et al. (1997) undertook the impact assessment of irrigation management
transfer in the Alto Rio Lerma irrigation district in Mexico. The study tested the hypothesis
that in general, Irrigation Management Transfer (IMT) had positive impacts on operational
performance, managerial accountability, O&M budgeting, overall O&M expenditures, cost of
water to farmers and agricultural and economic productivity. The study found that irrigation
management transfer has had very little impact, if any, on surface water allocation and
distribution and the use of groundwater. Changes, if any, in agricultural and economic
productivity and costs to farmers were related to the wider set of neoliberal agricultural and
economic reforms. On the other hand, there was strong evidence indicating that transfer
resulted in improvements in system maintenance and O&M cost recovery.
Vermillion (1997) conducted a study entitled ―Impact of Irrigation Management
Transfer: A Review of the Evidence‖. In this study he synthesized the evidence about the
impacts of irrigation management transfer programmes on the financial viability of irrigation
systems, the quality of irrigation operation and maintenance, the physical sustainability of
irrigation infrastructure, agricultural and economic activity and the environment. He
concluded that the irrigation reforms reduced the costs of the government and eventually the
29
cost of irrigation of the farmers increased. In this way the farmers made the more judicious
use of surface water. In this study, it was reported that the relationship between management
transfer and agricultural and economic productivity was less direct than the relationship
between transfer and O&M performance or financial viability. It was also found that there
was a substantial increase in water fee collection rates in the post-reform period. This increase
in water fee collection ranged from 30 percent to 80 percent. The study also concluded that, in
the year 1992/93 season, following the transfer, 70 percent of distributary canals and 60
percent of field-channel lengths were cleaned by farmer groups. As a result, 10 percent more
wheat and 8 percent more maize were grown in the dry season compared with previous years.
Oza (1998) observed that India had placed a great emphasis on development of the
irrigation sector right from independence. However, the problems of under-utilization, lack of
access by Tail-end farmers, poor maintenance and non-viability of the irrigation systems
persisted in the government owned surface irrigation schemes. It was also investigated that
small, privately owned irrigation systems (dug wells and tube wells) were more efficient and
provided more than 50 percent of irrigation water in India. In fact, the average water rate was
only 3 percent of the estimated net benefit from irrigation. Because of the low water rates and
poor recovery rates, revenue from the irrigation sector covered only 20 percent of the cost of
operation and maintenance, making the sector highly subsidized and non-viable. These
problems in the irrigation sector were more or less found in all states of India. Since water is a
major priority, farmers were constantly looking for alternatives.
Edward et al. (1999) analyzed that dilapidated and poorly maintained water
distribution infrastructure below the canal turnout; the system of farmer managed
watercourses was responsible for a significant proportion of overall system water losses. This
was specially the case in canal command areas where SCARP tube wells had been sited at the
watercourse Heads, but for which no provision for watercourse remodeling had been in
SCARP projects. The resulting water losses, reported are 40 percent or more, contributed to
the growing problems of water logging and were a primary cause for shortage in irrigation
supplies for Tail end farmers. They predicted that the new irrigation system and drainage
would both end the present crisis in the Indus Basin canal systems and brought about
sustainable benefits to farmers, including greater farm output and income. It would guarantee
30
a reliable supply of the minimum amount of water determined by the basic right, provide
opportunities for farmer organizations to plan ahead for purchases of additional water, and
reduce water losses as well as water charges. It was also believed that O&M would be carried
out more efficiently by the farmers.
Samad and Vermillion (1999) examined the impact of the partial management
reforms on the performance of irrigation system. The study was based on the methodology
developed by IWMI to examine the modalities of IMT in different country settings. The
performance of transferred system was compared with that of non transferred system. The
regression model was used to analyze trends in government investment with the annual O&M
costs/ha during the period 1985-95. The results showed that there were decline in
government‘s recurrent costs for irrigation during the period 1985-95 across all the categories
of schemes. The results indicated that there was a statistically significant declining trend in
government expenditure for O&M during the pre-IMT period. In the post-IMT period, there
was a slight reversal in the trend. In this study the regression model was used to analyze
trends in cropping intensities in different groups of schemes. The analysis indicated that there
were no significant differences in trends in cropping intensities in any of the four groups of
schemes in the period before and after transfer. Economic returns per unit of land and water
were measured in terms of gross value output (GVO) per hectare of cultivated land and per
cubic meter of water respectively.
Sarah et al. (1999) addressed the different inefficiencies in the irrigation system of
Turkmenistan. They found that irrigation efficiency was between 25 percent and 30 percent in
the system. Rehabilitation in the existing irrigation system could make substantial water
savings but the cost would be high. Estimates for rehabilitation for Turkmenistan put the
figure at $2000 per hectare which, for the republic as a whole, would be $3.5 billion. It
required a long term investment in the irrigation system of the country.
Wichelns (1999) noted that irrigation water policies could be enhanced by
considering the economic dimensions of farm-level decisions and public goals regarding
limited land and water resources. Policies that modified economic parameters could motivate
farmers to choose crops and irrigation methods that were consistent with public goals. Such
31
policies included water prices or allotments, subsidies for improving irrigation methods and
the removal of output price distortions that favoured crops with large water requirements in
water-short regions. Economic issues regarding water policy in the Nile Valley and Delta
were also included in the paper.
The author also argued that policy reforms could encourage farmers to use irrigation
and drainage resources efficiently by motivating improvements in the water management
practices, while generated revenue for operation, maintenance and capital replacement. The
author suggested that the design of appropriate policies could be enhanced by considering the
economic dimensions of farm-level irrigation decisions and public goals regarding limited
land and water resources. It was also concluded that farm-level costs of water could be
modified to reflect the delivery costs, opportunity costs and off farm effects of irrigation
decisions. Economic analysis of farm- level decisions regarding cropping patterns and
irrigation in Egypt demonstrated the potential role of economic parameters in the selection of
policies to improve resource use.
Facon (2000) argued that the notion of water delivery service and generalized service
orientation of institutions in the irrigation sector has become central in new concepts and
definitions of participatory irrigation management and irrigation management transfer. The
sustainability of the water users associations was depended on their capacity to provide an
adequate water delivery service that allowed the agricultural productivity to increase. In the
context of Asia, diversification of rice crops was a major issue for increased income by
farmers and improved agricultural and water productivity. The author reviewed the
implications of improved agricultural productivity and improved water productivity in terms
of required quality of water service, particularly in the case of rice and diversification of rice-
based farming systems. The author argued that concepts of irrigation management transfer /
participatory irrigation management transfer and modernization of irrigation systems
operation were therefore converging. However, there were still some substantial differences:
the infrastructural physical improvements which must be supported should be designed with a
view to improve equity and reliability of water delivery service and evolve towards increasing
levels of flexibility.
32
Amoah and Gowing (2001) examined a case study of irrigation management transfer
of a rice irrigation scheme in Ghana. The criteria used relate to agricultural, financial and
economic performance and environmental sustainability. The study showed that while both
cropping intensity and cultivated area decreased after transfer, the relatively high yields were
sustained. The average production cost after transfer decreased by about 7 percent from $827
per hectare to $774 per hectare after transfer. Most importantly, average net income increased
by more than 100 percent from $260 per hectare to $549 per hectare after transfer. Very high
financial self-sufficiency ratios coupled with low running cost achieved by the farmers‘ co-
operative led to the conclusion that transfer has resulted in better performance so far.
Dinar (2001) elaborated the implementation of existing concepts and strategies for an
integrated water management in Germany. In his paper, the author highlighted the politics
associated with various water sector management reforms at domestic and international
levels. At domestic level, reforms may include water pricing, water rights, and privatization.
At international level, arrangements may include, for instance, water allocation agreements
and handling of externalities (quantity and quality). Since politics of water reforms did not get
appropriate attention in the design and implementation of the reform process, this paper called
upon inclusion of political consideration in water sector reforms. Moreover, the paper
recognized the strong interactions between domestic and international politics in the water
sector, and suggested comprehensive rather than specific- localized approaches.
Hussain and Biltonen (2001) highlighted that agriculture sector in the Asia and
Pacific region faced the dual challenges of increased food demand and looming water
scarcity. The study found that the overall benefits from irrigation development were largely
skewed and unequal. The study examined that the pro-poor impact of irrigation differed
significantly from one setting to another. The extent of benefits depend on factors such as
land and water distribution, the quality of irrigation and infrastructural management, the
availability of inputs and support services, and water and agricultural policies. The study
suggested that there was no trade-off between equity/poverty and productivity. It was also
found that in settings with greater inequities in land and water distribution, as in India,
Pakistan and Bangladesh, low level of irrigation charges did not necessarily benefit the poor,
and it could be disadvantageous to the poor where charges lead to under-spending on O&M
33
and the system performance suffered. In this study, it was suggested that irrigation
interventions could be designed to re-distribute benefits in favor of the poor.
Barker (2002) presented a framework for examining the evolution of modern
irrigation development in South and Southeast Asia. Dissatisfaction with the performance of
these systems and pressures to reduce government budgets led to a period of irrigation
management reform. The growing scarcity and competition for water was leading rapidly to
the need that water should be treated as a resource and an economic good with a wide range
of uses that could benefit various members and sectors of society. Water must be allocated
equitably across sectors i.e. irrigation, domestic, industrial, and environment sector. There
must be coordination between farm and basin level management of water and between surface
and groundwater management. The impact of irrigation development on environment and
human health must be carefully analyzed.
Koppen et al. (2002) examined the ways to measure relative income poverty within
large scale canal irrigation schemes in India. The author assessed the different impacts of IMT
programmes on poor and non-poor farmers. Two different IMT programmes-the State-Wide
programme under The Andra Pradesh farmers‘ management of irrigation systems Act of 1999
(APFMIS) and the pilot programme under the participatory irrigation management (PIM) in
Gujrat were selected for the study. A sample of seven hundred land owning and tenant
farmers from seven water users associations were selected. The impacts observed were five
years of programme implementation in Gujrat and two years in Andra Pradesh. The results of
the study showed that there was an improved access to canal water after IMT for both farmers
at Middle and Tail end reaches of the command area. On an overall basis the average increase
was 15 percent to 25 percent. It was also found that there was an extension in irrigated area to
about 2 percent (average 0.66 ha).
Yercan et al. (2003) proposed performance criteria for irrigation according to the
situation of before and after irrigation management transfer in Turkey. The selected irrigation
schemes in Gediz river basin were examined and assessed for their physical and economic
performance criteria according to the situation of before and after management transfer
process. The analysis was based on time series; covering a period of 10 years (5 years before
34
transfer and 5 years after transfer). The results of the study showed that the transfer process
affected positively the rate of irrigation performance on overall basis. There was an increasing
tendency from 51-57 percent on an average rate of irrigation in the schemes studied. It was
also found that the rate of water fee collection was between 15-30 percent before transfer
process, and it was higher than 75 percent after the transfer and thus, cost recovery was
improved dramatically. The study concluded that public costs of operation and maintenance
begun to fall and would very likely continue to do so over the next few years. So, the positive
impact of transfer programme was reduction in the cost of irrigation to the government.
However, private costs had increased and would most likely to increase as more and more
responsibility was transferred to local agencies.
Abdelhadi et al. (2004) envisaged that the participatory management approach could
be successfully applied to a huge scheme such as the Gezira with large number of
smallholders under one administration. IMT was implemented as a pilot project and the
results were analyzed taking into consideration the interplay of the main factors in process
and the historical background and the attitude of the tenants. The average yield of four crops
before the project started (1999-2000) and in the first year of the project (2000-01) compared
with the scheme‘s average scheme. It was found that the crop yields, with the exception of
cotton, during 1999 were below the scheme‘s average and reduction was more pronounced for
wheat. The average increase in cotton ranged between 30-45 percent. The average yield of
sorghum increased between 36-310 percent. The cropping intensity was raised from 39-67
percent. The farmers were able to grow some new crops such as sweet potato, potato and
chicken peas in addition to expanding into vegetables. At the same time, there were some
fears about the consequences of immature transfer of responsibilities to farmers committees
without proper and sufficient training.
Penov (2004) determined the institutional alternatives and evaluated their impacts on
the irrigation system of Bulgaria. It was found that the current institutional settings could not
provide for sustainable water usage. The appropriation transactions regarding water were
regulated by a mixture of market (local monopoly) and hierarchy (state price intervention).
Three types of institutional options regarding irrigation in Bulgaria were discussed in the
paper. The first type aimed at improving coordination at the local level. Non-state
35
organization of irrigation water supply was recommended in villages with sufficient social
capital. In this respect, stimulating the development of small water user groups was seen as an
intermediate step toward establishment of water user associations. The second type of option
aimed at limiting the market imperfections (local monopoly). Inclusion of farmers'
representatives in the irrigation company management was recommended as a way of
increasing their bargaining position. However, this option was only feasible in areas with
well-established organizations of farmers. Finally, the third type of options aimed at
strengthening the external conflict resolution and sanctioning mechanisms.
Awosola et al. (2005) made an assessment of the economic, social and financial
performance of the Ogun-Oshun River Basin and Rural Development Authority‘s
(OORBRDA) irrigation projects in Nigeria. A structured questionnaire was used to gather
primary data from 73 participating farmers. Documented primary data on projects‘ activities
from the 1995/96 to 2001/02 seasons were summarized into social, economic and financial
performance indicators. In the Sepeteri project, service payment was enforced at a cost
recovery level of about 96 percent However, the project was not financially viable, because
only 29 percent of the expenditure was covered. Furthermore, the farmers did not have much
stake in determining the project's success with 67 percent social capacity level. The relative
profit level of irrigated cropping was 1:1.13, and did not present sufficient evidence that
farmers demanded (or preferred) irrigated cropping to rain-fed cropping. The project covered
about 50 percent of its total expenditure. The farmers did not have much stake in determining
the project's success, with a 33 percent social capacity level. The relative cropping profit
levels of 1:0.79 showed some evidence of higher demand or preference for irrigated land
compared to rain-fed cropping.
Doukkali (2005) reviewed and evaluated the institutional reforms in Morocco. The
study suggested that, considering their overall thrust and direction, the institutional reforms
undertaken in Morocco were truly remarkable. While these reforms have paved a solid
institutional foundation for promoting an economically responsive water sector, there were
still serious reform gaps, especially in areas such as groundwater regulation and supportive
institutions for irrigated agriculture. The reform experience of Morocco indicated that
although undertaking initial reform could be difficult, subsequent reforms were relatively
36
easier when the political opportunities for reforms provided by both endogenous and
exogenous factors were well exploited.
Hearne and Donoso (2005) offered a review of the institutional reforms in the water
sector in Chile. They analyzed that the factors that motivated institutional changes in Chile‘s
water management including ideology, transaction costs, interest-group behavior and path
dependency. The already observed institutional changes, such as transferable water rights,
water markets and urban water reforms were all significant. Furthermore, reforms were
delayed by the deliberate legislative process required for changes. However, institutional
changes during the period of military rule were rapid, ambitious and favored by private sector
and agrarian interest groups that supported their implementation.
Heyns (2005) highlighted the importance of the realization of political reforms within
a modern democratic framework called for wide ranging reforms in all sectors of the economy
to which the water sector was not an exception. Institutional reforms in the water sector were
undertaken with an overall aim of introducing integrated water resource management as a
durable solution to the water challenges of the arid environment prevailing in Namibia. The
reforms included the development of a new national water policy to manage and regulate
activities in water sector through institutional changes. It was also found that although
institutional reforms in the water sector were necessary to meet the demands of a new nation,
they could not succeed without the required level of skills and capacity both within and
outside water administration. While it was relatively easier to formulate new policies,
promulgated legislation and create new organizations, it was very difficult for an emerging
country to develop quickly the human capacity necessary to handle the reforms, especially
when inadequate funding constraints created a conflict between resource development and
capacity building. As a result, very little progress had been made to address the real needs of
the water sector in Namibia.
Livingston (2005) presented a framework to understand the potential and the need for
change in water institutions. The pressure for institutional change could be analyzed at the
micro and meso levels. At the micro level, the model pointed to how evolving subjective
interests and changing objective realities can be combined to shape the forces for institutional
37
change. At the meso level, the model focused on the probability that pressure at the micro
level would result in actual change. It was observed that the role of political agents and
structure of institutions in the status quo was critical. The concepts of nesting, path
dependency and institutional transaction costs had been used at this level of change.
McKay (2005) reviewed the water institutional reforms in Australia. It was found that
the reforms initiated in 1995 were notable for their comprehensiveness, fiscal incentives and
clear and time bounded targets to be achieved. Although water institutions in Australia had
undergone remarkable changes, however, there were still issues and challenges inherent in
reform process in Australia. It was found that Australia needed further reforms; its recent
reform experience provided considerable insights into the understanding of both the theory
and practice of water institutional reforms.
Saleth and Dinar (2005) examined the conceptual, analytical and theoretical aspects
of water institutional reforms and a synthesis of the main findings from the reform
experiences of six countries: Australia, Chile, Morocco, Namibia, South Africa and Sri Lanka.
Based on the latest developments in the literature on the subject, this paper presented the
analytics of unbundling water institutions to show their endogenous and exogenous linkages,
the transaction cost approach as a diagnostic framework for understanding the role of factors
affecting water institutions, and a stage-based perspective to provide insights into the internal
mechanics and dynamics evident in the process of water institutional change. Using this
analytical framework and theoretical approach, the paper also identified a few practically
relevant principles for reform design and implementation. Based on a review of individual
country reform experiences, the paper also synthesized reform theories with actual practices
by providing anecdotal evidence for various theoretical postulates and practical reform
principles.
Samad (2005) examined the institutional reforms in water sector in Sri Lanka by
comparing those observed during the 1980s with those proposed during the 1990s. It was
found that the earlier reforms focused on the irrigation sector that yielded quicker benefits and
low political risks. The later reforms covered macro institutions and the whole water sector
where the benefits were gradual and less visible but with the high political risks. As the earlier
38
reforms were packaged as part of larger investments, they had built-in incentives and strong
proponents. The recent reforms not only lacked such conditions but also faced an
ideologically charged hostile environment. The public at large remained passive with the real
intent of the proposed reforms especially the issue of creating a public support to the ideology
and politically based opposition.
Smajgl et al. (2005) developed a conceptual framework for water reforms in
Australia, and used an Applied General Equilibrium (AGE) model to investigate the impacts
of potential water reform. The first part of this paper was regarding the application of soft
systems methodology to develop a conceptual model of water reforms for irrigators. The
second part of the paper developed a quantitative model of water reform and presented the
results of scenario analysis performed by the AGE model. Specially, the outcomes of an
important water reform option were shown for economics, social and environmental
objectives. It was assumed that a linear reduction in the use of ground water was necessary to
achieve an optimal ground water level. The results of the study showed that higher levels of
restriction lead to significantly higher efficiency gains but also large welfare decline. A
doubling of groundwater table would lead to an increase of water use efficiency by up to 46
percent while, the highest welfare loss was 25 percent. An increase of the groundwater table
by 33 percent would lead to an efficiency effect of 1 percent and the highest welfare loss was
less than 3 percent. Connected with an increase of the groundwater table by 25 percent was no
effect at all.
Zhovtonog et al. (2005) analyzed that in the beginning of 1990s the period of
transition from a central planning economy to a market economy started in all Central and
Eastern European countries (CEEC). Many common issues in the agriculture and water
management were recognized. In irrigation sector, the majority of CEEC faced similar
problems like decrease in agricultural production, deterioration of irrigation and drainage
infrastructure. The process of reforms in agriculture and water sector in different countries
was initiated with respect to local natural conditions, traditional farm practices as well as
institutional and legislative developments. He studied the reform process and drew some
lessons regarding the IMT. It was found that intensity and shape of the reform process were
different from country to country according to the prevailing economic and political structure.
39
In some countries like the Czech Republic, Germany or Poland, radical restructuring of the
irrigation sector took place, while in others like Solvenia and Macedonia, some governmental
organizations still played an important role in the management of irrigation system. In various
other countries, like Bulgaria, Romania, Russia and Ukraine, the process of reorganization
was just started. He suggested that in order to enhance the irrigation reform process it was
vital to clearly specify the roles, functions and responsibilities of the various actors involved
in the reform process. Depending on the stage of the reform process and on the economic
situation at farm level, governments would have to retreat step by step from involvement in
management and operation and maintenance functions.
Bandaragoda (2006) synthesized studies in five selected Asian countries on their
water policy reform initiatives. Of the five countries, China stands out as the country that has
derived the most from on-going global efforts in promoting water sector institutional reforms
and the concept of integrated water resources management (IWRM). China emerged as the
leader in adapting these concepts to suit the context of the country. Advanced stages of water
development in many parts of the country and increased water shortages due to rapid
economic development have prompted China to forge ahead in the search for institutional
solutions to make the water sector more productive, and the management of water resources
more sustainable. In the other selected countries, efforts to replicate the models of developed
countries without much adaptation and due reference to their stages of development have
generally failed.
Molden et al. (2007) concluded that effective irrigation reforms could provide the
environment for productive and sustainable agriculture that is vital for economic growth and
uplifting lives of the people and keeping them out of poverty. Poorly managed irrigation could
have the similar effect. Irrigation performance assessment was an important management tool
to aid in providing sound service. Performance assessment in irrigation and drainage was the
systematic observation, documentation and interpretation of activities related to irrigate
agriculture with the objective of continuous improvement.
Bandyopadhyay et al. (2007) analyzed the impacts of irrigation management transfer
in Philippine. It was found that the motivation behind IMT was that it would reduce
40
government responsibilities for operation and maintenance and simultaneously increase
farmer‘s supervision over water use. By lowering government expenditures and strengthening
local governance, IMT was expected to have a long-term impact on the country‘s agricultural
and natural resource sectors. With an IMT contract, the water user associations could make
better decisions regarding water delivery and timeliness and could organize themselves to
resolve conflicts and maintain infrastructure. Without local control, associations have to wait
for the national agency to come in and undertake repairs – with IMT they perform repairs as
and when needed. The results of the study also showed that the implementation of IMT was
associated with an increase in maintenance activities undertaken by irrigation associations.
While Irrigation Associations with and without IMT contracts both undertake canal
maintenance, the frequency of maintenance in IMT was higher. IMT areas also had higher
rice yields to the extent of 2 to 6percent relative to non-IMT areas. The analysis also showed
that IMT was associated with a reduction in technical inefficiencies in production. Thus,
increasing local control over water delivery did appear to help with farm productivity.
Madhav (2007) identified the factors contributing to the inefficiency in the canal
irrigation system in India. He found that the persistent under- funding of O&M works had
resulted in rapid deterioration of the network and large conveyance losses. The resources were
thinly spread over a large number of projects, leading to substantial time and cost-overrun. He
also analyzed that poor water management hindered the delivery of adequate, reliable and
equitable irrigation. Farmers in the Head reaches of major and medium irrigation schemes
drew water far in excess of their allocation, and as a consequence, water did not flow into
areas downstream. The solution as recommended to the Andhra Pradesh Government by the
World Bank was to focus on cost recovery and decentralizing irrigation management by
vesting greater powers and responsibilities in water users. It was believed that this would lead
to improvement in quality and cost efficiency of irrigation management.
41
2.2 Selected Studies Related to Pakistan
Radosevich (1975) worked out the role of water users organizations for improving
irrigated agriculture in Pakistan. He concluded that Pakistan has no institutionalized system of
water users associations by which her farmers could jointly pursue optimizing mutual tasks.
Many of the problems faced by the farmers, particularly the small farmers, can be partially
solved by providing them an opportunity to formally organize with their neighbors to increase
agricultural production by improving water management activities. The water user
associations could become the nucleus of mutual on-farm activities pursuing objectives of
equitable distribution of water, resolving disputes, watercourse rehabilitation and collection of
irrigation fees and assessments.
Haq and Shahid (1997) presented a brief overview of Pakistan‘s irrigation system
and the rural society as wells as the major issues facing irrigation management in Punjab.
They summarized the strategies and models proposed by various agencies for participatory
irrigation management and evaluated their main strengths and weaknesses. The authors
mentioned that irrigation water demand in Pakistan increased tremendously over the past
three decades due to agricultural development far beyond the designed parameters. The
system and the supply constraints limited the capacity of the Punjab Irrigation Department
(PID) to respond effectively to the increased water demand. The changing socio-political
situation and general decline in discipline of the society added to the problems of irrigation
management. The paper also discussed major issues and options for improving irrigation
performance. It was recognized that greater farmers‘ participation in irrigation management
was of considerable value and needs to be pursued. The extent and arrangements for farmers‘
participation, however, depend on local environment. The patterns of other countries could
serve as useful models but did not necessarily had universal application. Past experience
suggested that in Pakistan, farmer‘s participation could be done the best through gradual and
phased process.
Latif and Zaman (1998) identified the constraints in the performance of irrigation
systems of Indus Basin with special reference to the performance of the system and equity of
water. The main issues discussed were, reduced capacities of canals and distributaries, poor
42
performance of the system, deteriorating institutional structure and inequitable distribution of
irrigation water. It was found that the annual water supply varied from 248 mm to 398 mm
per unit area against designed value of 437 mm. Moreover, less water was supplied in winter
season than summer. It was also concluded that at canal command level the informal
operational practices and role of operators seemed to be the main reason for inequitable
distribution. At distributary level, illegal abstraction of water and location characteristics was
important factors affecting equitable water distribution.
Nakashima (1998) conducted a study on Pakistan‘s institutional reforms in the
irrigation sector in Punjab province. Based on the past and present experiences in water users
organizations, a few necessary conditions for user governance of irrigation water were
discussed. He found that irrigation fees had been sufficient to cover operation and
maintenance (O&M) costs until the irrigation sector started to deteriorate in the 1970s. Due to
weakened discipline, the collection of irrigation fees from the farmers declined, and revenues
fell short of government O&M expenditures. The gap between recoveries and expenditures
through water fees was 44 percent in 1992, which was high and increasing. Consequential
deterioration of irrigation infrastructure, together with eroding institutions, had brought
irregular water distribution to the canals, resulting in unequal irrigation water distribution
among farmers. Inequity in irrigation water distribution was a major problem for farmers. The
irrigation sector was suffering from these and other similar problems.
Jehangir et al. (1999) found that the government of Pakistan was spending heavily on
the operation and maintenance of the irrigation system yet shortage of funds was a major
reason for deferred maintenance, which threatened the operational integrity of the irrigation
system. The shortfall in O&M funding was estimated to be more than 24 percent in 1993. The
poor O&M had direct effect on the productivity of agriculture; indirectly it affected the whole
economy. The allocation of funds for the increasing O&M costs was becoming a problem for
the Government of Pakistan every successive year. This paper aimed at estimating the level of
operation and maintenance expenditures of the H-4-R Distributary (Bahawal Nagar) and the
situation of the Aabiana collection and the extent of its leakage through different means. The
results of the analysis of Aabiana collected and O&M expenses incurred showed that the
Aabiana collection was almost always in excess to the operational and maintenance expenses
43
incurred on H-4-R Distributary. From the analysis, it was clear that the real cause of low
Aabiana collection was Aabiana under-assessment. So Aabiana assessment procedure should
be improved. It was anticipated that if the activities of Aabiana assessment, collection, and
incurring of O&M expenses were with farmer organization, it could improve since both
would become interdependent. High Aabiana recovery would also lead raise the ability of the
farmer organization to spend more to improve system O&M.
Mirza et al. (2000) concluded that both national and international experience
suggested that the small irrigation schemes, fully managed by the water users could improve
the irrigation system O&M and bring equity in water distribution for all water users. This in
turn could help in increasing crop productivity and environmentally sustainable irrigated
agriculture. However, successful implementation of this process needs political will, legal
framework, independent collective decision making by Farmer Organizations (FOs) and
effective and continuous institutional support from relevant agencies. They also found that the
gradual deterioration of the irrigation systems throughout the world exposed serious
institutional deficiencies and government failure to deliver the services in most water
resources systems. It was also examined that in most of the developing countries financial
crises and inability of government to deliver services was visible. This included lack of
motivation and accountability of agency staff, high levels of political interference and rent
seeking and inadequate concern for needs of water users. On the other hand, without reliable
and equitable supply of water, users were not ready to share the ever increasing costs of
operation and maintenance (O&M). The options left behind were to involve the users of the
system in sharing some of the responsibilities of O&M for sustained and improved
agricultural production.
Rinaudo et al. (2000) investigated the nature of the existing economic rent in public
irrigation systems. The author proposed a conceptual framework to analyze the distribution
between private and public actors involved in irrigation management. A case study was
conducted in Pakistan's Indus basin to quantify the overall level of rent granted to the
irrigation sector and to show how farmers compete for the appropriation of the greatest
possible share of this rent. The study found that rent-seeking activities were not confined to
wealthy and politically influential farmers only but small and medium-size farmers also
44
interfere in water distribution, especially when they were located in the upper reach of the
hydraulic system. It was also highlighted that rents were shared between three types of actors:
politicians, officials of the irrigation agency and water users through a system of
administrative and political corruption. As a consequence, a significant share of the rent
intended to benefit farmers was transferred out of the agricultural sector, which was
detrimental to the level of investment in the sector and to its productivity.
Tahir and Habib (2001) examined the spatial variation in production across canal
commands using gross production indicators i.e. Gross Value of Production (GVP) per unit of
land and GVP per unit of water. Given the data constraints, Punjab province was selected for
the analysis, which consisted of major network of 12 inter-linked and a total of 23 canals out
of 45 canals of Indus Basin Irrigation System (IBIS). The analysis was performed at the canal
command level. In the study, GIS application was developed and validated to convert district
level information into canal command (hydraulic unit) level. Punjab province has 35 districts
and 23 main canals. A big variation in cropping intensities across Punjab canals was shown
by the secondary data, ranging from less than 60 percent to 160 percent, annually. In Kharief
season, GVP per unit of CCA varies with a ratio of 1:10 (Rs. 1,451 per hectare to Rs. 13,836
per hectare), and GVP per unit of CA varied with a ratio of about 1:4 (Rs. 4,368 per hectare to
Rs. 15,649 per hectare). In Rabi season, GVP per unit of CCA varies with a ratio of 1:4 (Rs.
1,566 per hectare to Rs. 6,258 per hectare), and GVP per unit of CCA varied with a ratio of
about 1:2 (Rs. 6,251 per hectare to Rs. 9503 per hectare). In Kharief season, GVP per unit of
water varied with a ratio of 1:6 (Rs. 0.21 per cubic meter to Rs. 1.47 per cubic meter). In Rabi
season, GVP per unit of water varies with a ratio 1:6 of (Rs. 0.39 per cubic meter to Rs. 2.41
per cubic meter). Annual GVP per unit of CCA among 23 canal of Punjab varied with a ratio
of about 1:5 (Rs. 3844 per hectare to Rs. 18326 per hectare). Annual GVP per unit of water
available varied with a ratio of 1:5 (Rs. 0.35 per cubic meter to Rs. 1.57 per cubic meter).
Rinaudo (2002) examined that corruption could determine the allocation of water in a
large public canal irrigation system. The socio-economic characteristics of farmers who
participated in illegal exchanges were analyzed using hydraulic and socio-economic field data
collected from 420 canal outlets of Southern Punjab irrigation system in Pakistan. The
analysis showed that corruption did not only involve economically and politically powerful
45
farmers but it also concerned the lower social segments of rural society. He concluded that
corruption in Pakistan‘s irrigation system arose from the scarcity of a resource, which was
priced far below its marginal value. The under- pricing of water generated a demand for this
resource that exceeded the available quantity in system, thus creating economic incentives for
farmers to resort to illegal means for obtaining more water than their official quota. It was
also concluded that the irrigation agency officials illegally supply more water to farmers who
offered bribe to them. Water corruption without involvement of department officials was quite
difficult.
Latif and Pomee (2003) designed a study to evaluate a farmer-managed distributary
in southern Punjab under the IMT period. As a result of these improvements imparted by the
FO in system management, the extent of irrigated area was increased on an average by 6 to
percent, even under severe drought-like conditions prevailing in the country during those
years. It was also found that cost recovery increased by an amount of 14 percent for summer
and 23 percent for winter growing seasons, respectively, from the irrigated area of the
distributary. Based on the results of the study, it was concluded that there was proportionate
and equitable distribution of irrigation supplies particularly to Tail end water users. The extent
of irrigated area increased, on an average, by 6 percent to percent and the cost recovery by 14
percent to 23 percent during the post transfer summer and winter seasons, respectively.
Lashari et al. (2003) suggested that the participation of beneficiaries (water users)
was one of the best tools to ensure as well as gauge the reliability of water delivery and equity
in water distribution. Based on the results, they concluded that the institutional reforms as
envisaged by ensuring the participation of farmers in irrigation sector was the only option
towards an integrated water resource management where irrigation and drainage function
simultaneously under the umbrella of one institution and active involvement of beneficiaries.
Dinar et al. (2004) developed an approach to assess the political risk associated with
implementation of institutional reforms in the water sector. The approach consisted of a two-
tier process to assess the institutional feasibility of reform implementation. The first tier was a
structured analysis of power distribution among the power groups interested in the outcome of
the reform. The second tier was a Delphi process, reflecting the opinions of experts. The
46
approach was applied to the case of the National Drainage Program Project (NDP) in
Pakistan. Several hypotheses regarding likely progress were tested, using the feedback
provided by a panel of experts in the Delphi process. It was found that reform process was
implemented at slower pace and low level of education among the farmers was a hurdle in
implementing the reform process.
Johnson III et al. (2004) examined the range of institutional options available to
manage the changing irrigation sector of the 21st century. The paper described the various
institutional approaches that were being used and explored the dimensions of the national
contexts within which they were being implemented. Lessons and experiences from Australia,
France, Mali, Mexico and New Zealand were shared by the author. Drawing from experience
in different countries, the paper examined performance as related to the Pakistan‘s‘ context
and organizational framework. The study also provided a guideline for management transfer.
It was perceived that in Pakistan, replacing the Punjab irrigation department (PID) with
Provincial irrigation authority (PIDA), creating Area water board (AWB), formation of
former organizations (FOs) depend upon water charging system and sustainable cost
recovery. It was necessary for the stakeholders to pay water charges to cover the O&M costs.
The author concluded that in Pakistan, the process of irrigation management transfer (IMT)
would be completed in next 20 years and irrigation in Pakistan would be decentralized. It was
suggested that the institutional reform must be the result of a specific policy decision made by
the senior administrators and policymakers in the country. It could not simply be a program
agreed to under pressure from a donor but requires high-level involvement and commitment
from the public also.
World Bank (2005) made an analysis that the water economy of Pakistan depend
fundamentally on a gigantic and complex hydraulic infrastructure system. There were a set of
related challenges which need to be addressed – how to maintain what has been built. It was
also found that many elements of the vast hydraulic system now reached the end of their
designed lives, and have to be re-built. There is an enormous backlog of deferred
maintenance. Most recent irrigation and water supply ―investments‖ from donors, including
the World Bank, had been for the rehabilitation of poorly maintained systems. There was no
systematic Asset Management Plan at either the Federal or Provincial level which described
47
the condition of the assets, the requirements for replacement, rehabilitation (or retirement) and
operations and maintenance of the whole system.
Hussain et al. (2006) reviewed a synthesis of key lessons, messages and examples of
better practices in participatory irrigation management (PIM) in the world. The paper covered
a fairly wide range of countries and regions where PIM reforms were being implemented. The
study covered a wide variety of hydrological and agricultural environments and irrigation
systems including small, medium and large systems, and systems with short and long history
of PIM reform experiences. The study explored the links between irrigation and poverty
alleviation in six Asian countries (India, Pakistan, Bangladesh, China, Vietnam and
Indonesia) with the aim to determine realistic options for increasing returns to poor farmers in
the low productivity irrigated systems. The study was based on primary data collected from
over 5400 rural households covering 26 irrigation systems, supplemented with reliable
secondary data and review of global literature on the subject. One of the main conclusions of
the study was that irrigation did indeed significantly reduced poverty as measured by the
household income. Poverty outside of irrigation systems in nearby non-irrigated settings was
much higher than that within irrigation systems. The author concluded that pro-poor impact of
irrigation differed significantly from one setting to another depending on factors such as land
and water distribution, the quality of irrigation and infrastructural management, the
availability of inputs and support services, and water and irrigation policies. The study also
concluded that inequity and insecurity in access and rights to land and water were bad for
both productivity and poverty. It was also found that in South Asia institutional reforms in
irrigation sector were moving at snail‘s pace and only on limited scale. The study concluded
that, in South Asia, unless irrigation reforms were sharpened with a pro-poor focus the poor
might be bypassed. Irrigation reforms were likely to generate significant benefits for the poor
where land and water were less inequitably distributed.
Lashari (2006) observed the two elements of equity on the basis of results collected in
the pre-transfer period. External equity issues were regarding water allocation and delivery
between different distributaries. Internal equity issues were regarding how water was shared
among watercourses along a canal. He found that in the two canals with favorable water
deliveries at the Head there was no noticeable Head-Tail difference, and all the farmers got at
48
least designed discharge during the peak of the summer season. The third canal which got
close to designed discharge showed a marked disparity between Head and Tail, with Tail-
enders more or less deprived of reliable water. He suggested that greater internal equity of
water distribution be achieved when the internal mechanism was made stronger and farmer
organizations be given a full responsibility for operation and maintenance.
Sarwar (2006) studied the on going reform process in the Province of the Punjab. He
analyzed the role of donors, the influence of existing institutions, the Canal and Drainage Act
and other organizations like PID as well as role of elites with PIDA. He found that all the
agencies had major influence on institutional and organizational change. The conclusions
were based on the historical information about the reforms, the influencing factors before and
after their introduction, the implementation process, and the current functioning of water
management organization and the current situation of reforms. He found that the pressure
from the donors for reforms, particularly from the World Bank, was based on increasing
financial crises and big gap between revenue and expenditure. He mentioned that top-down
strategy was adopted in the introduction of donor driven reforms, regarding the supply
induced economic changes under the pressure from international financing agencies. The
anticipated changes did not yet occur, due to the opposition of the existing organization i.e. the
PID. Different stakeholders especially the staff of old irrigation departments and the elites
were opposing the reforms before their introduction and later were causing the reforms
process to slow down. The study showed that the supply-induced change had been slow and
not successful due to lack of support from the powerful stakeholders. Bureaucratic elites of
PID have been able to significantly affect the reform implementation process to the extent of
change in ‗model‘ with change in personalities. He further added that the newly formed PIDA
(Punjab Irrigation Development Authority) and the reforms were facing many difficulties due
to weak legal framework and bottlenecks in the PIDA Act 1997. If the reforms were
implemented sincerely according to the provisions outlined in the legislation, the process
would go in the right direction. The inclusion of Canal and Drainage Act in the new act added
further complexities for PIDA in the new setup. It was still questionable that the old Act
would be completely drawn out for better functioning of the reformed institutions.
49
2.3 Summary
The main focus of this chapter was to review past studies conducted to determine the impact
of institutional reforms in the irrigation sector of the world as well as of Pakistan. The review
of literature showed that most of the studies were directly or indirectly related with the study
in hand. Each study had specific features on the basis of objectives and methodology adopted;
however, the findings were more or less same. The national and international experience
reflected that impacts of irrigation reforms in the world had both positive and negative
implications for small, medium and large farmers. It was clearly reflected that equity in water
distribution was achieved by the involvement of farmers in the decision process. However, it
differed significantly from one setting to another depending on factors such as land and water
distribution, the quality of irrigation and infrastructural management, the availability of inputs
and support services, and water and irrigation policies. In some countries like Mexico, USA,
Turkey and Egypt, the reform process remained successful.
As for Pakistan, many studies indicated that more than a century old irrigation network
supervised by the Punjab Irrigation Department had not been working according to the
satisfaction of the stakeholders. It remained unable to reduce the Head-Tail equity in the
distribution of water. The gap between O&M expenditures and cost recovery was increasing
with the passage of time. Consequently, the government of Pakistan introduced institutional
restructuring in the irrigation sector of the Punjab. These studies found that the IMT, in
general have both positive as well as negative implications on operational performance,
managerial accountability, operation and maintenance of the system, cost of irrigation water
to the farmers, and agricultural productivity.
50
CHAPTER 3 METHODOLOGY
Analytical study comprises of systematic and appropriate techniques for analysis. The
selection of sample, data source and methodology is important to analyze, verify and describe
the relationships. The finding and analysis of data comprising qualitative and quantitative
variables need in-depth interpretation. The data presentation and dissemination leads to
successful completion of the study. Keeping in view the objectives of the study, following
research methodology was adopted.
3.1 Selection of Study Area
The area of Lower Chenab Canal LCC (East) was selected as study area. The process of
irrigation reforms was initiated as a pilot project and completed in the area of LCC (East). As
the main objective of study was to assess the impact of the irrigation reforms in terms of
improving water delivery, equity in water distribution and overall agricultural productivity.
Therefore, based on the above consideration and to meet the objectives of the study, the LCC
(East) was selected as a case study on account of the reason that first phase of reform process
was initiated and completed on this canal division. It has four canal divisions. These are:
1. Khanki Division
2. Upper Gogera Division
3. Lower Gogera Division, and
4. Burala Division
The LCC (East) irrigates the fertile land of Gujranwala, Hafizabad, Sheikhupura, Faisalabad,
and Jhang districts.
3.2 Characteristics of the Study Area
The characteristics of the study area are divided in to two parts. In the first part a brief
description of the districts irrigated by LCC (East) is given, and in the second part specific
characteristics of the LCC (East) are given.
51
3.2.1 A Brief Description of the Districts in the Study Area
A brief description of the districts which are being irrigated by LCC (East) and where
irrigation management has been transferred to the stakeholders is given below. The districts
include Hafizabad, Gujranwala, , Sheikhupura, Faisalabad, and Jhang.
Hafizabad District
Hafizabad was given the status of district in July 1993. It is bounded on the north by Sialkot
district, on the east by Gujranwala district, on the south by Jhang and Faisalabad districts and
on the west by Sargodha district. The total area of the Hafizabad district is 2,367 square
kilometers, of which 80 percent is under cultivation. It is generally plain and there is no hilly
area in the district. The river Chenab passes through the district of Hafizabad. There are some
marshy areas along the river side. Nature of land is sandy and clay-loam. The entire area is
irrigated through canals and tube wells. The sub-soil water is almost sweet (fit for drinking
and irrigation). The LCC (East) irrigates the whole district through branch canals.
The climate of the district is hot for most of the year. The average annual rainfall in the
district is 790 millimeters (GOP 1998). During summer, temperature goes up to 45 degree
centigrade with minimum 20 degree centigrade. The average rainfall per month ranges from
50 to 75 millimeters. The major crops of the district are rice, wheat and sugarcane. The best
variety of Basmati rice (Karnal) is cultivated in the fertile lands of Hafizabad district.
Gujranwala District
The district of Gujranwala is located at 700 feet above the sea-level. It has an area of about
5,988 square kilometers (GOP 1998). The district is bounded on the north-west by Gujarat
district, on the east by Sialkot district, on the south by Sheikhupura and Faisalabad districts
and on the west by Jhang and Sargodha districts. The district has extremes of climate. The
summer season begins in April and continues still September. May, June and July are the
hottest months. The mean maximum and minimum temperatures during this period are 39°C
and 26°C respectively. The winter season begins in November and continues till March.
December, January and February are the coldest months. The maximum and minimum
temperatures during this period are 20°C and 7°C (GOP 1998). The monsoon usually begins
52
in July and continues with usual muggy spell until the middle of September. It is one of the
most prominent districts of rice growing areas in Pakistan. Major crops grown in this district
are rice, wheat and sugarcane. In some areas vegetables and fruits are also grown.
Faisalabad District
Population wise, Faisalabad is the third largest district of Pakistan and second largest of
Punjab. It is bounded in the North by Gujranwala and Sheikhupura Districts, in the East by
Sheikhupura and Sahiwal districts, in the south by Sahiwal and Toba Tek Singh districts and
in the West by Jhang district. It has an area of 5,856 sq. km. and population of approximately
3.54 million people, (GOP 1998). This district consists of six sub-divisions and Faisalabad
city is the districts Headquarter. Out of total area of 1.44 million acres of this district, 1.15
million acres of land are irrigated through canals (GOP 1998). Rest of the area is either Barani
(Rainfed) or cultivated through tube wells. The district has flat alluvial plain formed by
Chenab and Ravi rivers. The river Ravi flows along the south eastern boundary of the district.
The land close to the river is relatively lower than that away from the river towards the west.
The climate of the district touches two extremes. The maximum temperature in summer
reaches up to 50°C or 122°F. In winter, it may, at times fall below the freezing point. The
mean maximum and minimum temperature in summer are 39 and 27°C respectively and in
winter, 21 and 6°C respectively (GOP 1998). The summer season starts from April and
continues until October. May, June and July are the hottest months. The winter season, on the
other hand, starts from November and continues until March. December, January and
February are the coldest months. Faisalabad district is un-parallel for its agricultural
productivity. Major crops grown are wheat, rice and sugarcane and in some areas cotton is
also cultivated.
Sheikhupura District
Sheikhupura city is located 32 km west of Lahore, and is linked to the other regional centers
of Punjab. Sheikhupura district is bounded on the north by Gujranwala and Sialkot districts,
on the east by Lahore and Kasur districts, on the south by Sahiwal and on the west by
Faisalabad. The Sheikhupura district is spread over an area of 5,960 square kilometers (GOP
53
1998) with a population of more than a million people. District has extreme climate; the
summer season starts from April and continues until October. During the summer season,
temperature ranges from 30 to 45 degrees Celsius. The winter season starts from November
and continues until March. December and January are the coldest months with a mean
minimum temperature of 5 degrees. The rainfall is 500 mm per year. The mean minimum and
maximum humidity during winter is 37 percent and 84 percent, respectively. There is a
network of canals in the district for irrigation. The Upper Chenab Canal and Lower Chenab
Canals are two major perennial canals, which supply water for irrigation. Major crops are rice,
wheat and sugarcane. Sheikhupura is famous for Basmati rice production in the world.
Jhang District
The district of Jhang is bounded on the north by Sargodha and Gujranwala districts, on the
west by Mianwali, on the south by Multan and on the east by Faisalabad. The surface of the
district presents three levels: on the extreme west are the high dunes of the desert Thal; in the
center are the two low-lying valleys and on the extreme east is a portion of the old Sandalbar.
The rivers Chenab and Jhelum pass through the district. The climate of the district is hot in
summer and cold in winter. The maximum and minimum mean temperature in summer is 45.5
degree centigrades and 29 degree centigrades and dust storms are common during the summer
season. The main crops are wheat, cotton, sugarcane and grams. Land is irrigated by canals
and tube wells. The total area irrigated by all sources is 126 thousand acres (GOP 1998).
3.2.2 Specific Characteristics of the LCC (East)
Lower Chenab Canal (East) off takes from the left flank of Khanki Headwork which is
constructed at the river Chenab. It was constructed during the last decade of 18th century and is
about 114 old years. The designed cropping intensity of the system is 40 percent to 75 percent
with water allowance of 1.52 Cs/1000 to 2.85 Cs/1000 acres. The cropping intensity has increased
to 135 percent. The system irrigates about 3.04 million acres (123 million hectares) of cultureable
command area located in the system (GOP 2006). Table 3.1 shows the salient features of the LCC
(East) irrigation system of the Punjab.
54
Table 3.1: Salient Features of the Selected Irrigation System