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Evaluation of water management in irrigated croplands


A.K. Chakraborti

Water Resources Group, National Remote Sensing Agency
Hyderabad, India

Abstract

Declining investment in the irrigation sector, increasing environmental concerns and long gestation period in turning the irrigation potential into a functional system are shifting the focus to improving existing irrigation systems rather than creating more potential. System performance monitoring, evaluation and diagnostic analysis are the keys to an improved irrigation management. One of the system performance monitoring matrices is to evaluate water demand and supplies in the irrigation system and identify the water deficit and surplus areas for corrective measures. Satellite remote sensing provides a tool to arrive at crop acreage and net irrigation water requirements at canal level for each crop season and thus meet the system performance monitoring criteria. A case study is cited on how to use this modern information technology tool.

Introduction

Approach

Cropping systems are planned based on available soil, climate and water resources to obtain maximum production. Management of water supplies for irrigation is one of the most critical water-related problems especially in arid and semiarid agricultural lands. The objective of efficient and sustainable water management in an irrigated cropland is to ensure optimum linkage between water availability and water demand. This is best done by matching demand for water in terms of crop water requirements and available water supplies in time and in the required quantity.

Remote sensing and geographic information system data requirements

Application of remote sensing techniques has the potential to provide irrigation command resource inventory. The following information can be extracted from remote sensing data for any canal system:

Besides this, other basic information needs to be collected from an irrigation project or an operation manual to create a database in geographic information system platforms:

Tools for evaluation

The following three steps are required:

  1. Estimation of crop areas. This is done by multiple-date satellite-based digital estimates of the main land-use and land-cover classes, including crop types and acreage. To evaluate the accuracy and reliability of satellite-derived information, a comparison can be made with similar information obtained from the agricultural census abstracts kept by the government departments.
  2. Estimation of irrigation water requirements. Monthly crop water requirements for all the main crops using daily pan-evaporation data and crop coefficient values during the various growth stages to calculate the water requirements of each crop.
  3. Use of efficiency factors for water conveyance, field applications. Total irrigation water requirements are estimated by adding up monthly demand for irrigation requirements for all crops during all the crop seasons (rainy season, winter and summer).

Assessment of water availability

The estimation of the irrigation water available from canals is straightforward. Daily flows into canals are totalled up to give monthly and annual supplies. The total groundwater draft is estimated from the tube-well or dug-well inventory data, by adopting suitable norms for dug wells and wells fitted with pump sets. Irrigation tanks and ponds are also sources of irrigation in the command area. Satellite data provide a very precise picture of the water spread of tanks and of the area irrigated by each tank. With this information, and following established norms, the total water available from tanks and ponds for irrigation can be arrived at.

Expected results

Satellite data thus provide spatial information about the main crop types and crop area estimates which are used to assess total irrigation water requirements as described above. They also provide information for the irrigation cropland inventory classified by source, i.e. canal, well or tank. Monthly canal supplies are then compared with total monthly demand to identify any surplus or deficit in any segment of the irrigation command on a canal system basis. A similar comparison is made between supply from all irrigation sources (canals, wells and tanks) and the total demand estimated from all the crops, irrespective of source of irrigation in the command area, on a monthly, seasonal or annual basis.

A diagnostic analysis can be made based on the above procedure to know precisely:

Ultimately, remote sensing and geographic information techniques help in the evaluation of the irrigation system performance and in redefining guidelines to improve water use efficiency and crop productivity on a sustainable basis.

Case study

Study area and satellite data

Study area

Geographical co-ordinates

Satellite data used

17 minors of the Mahendragarh canal distributary in Haryana State

28o 9'20" - 28o 21' 57" N Lat.

76o 4'23" - 76o 13' 7"E. Long.

IRS-1B LISS II/3.10.1992
- for kharif season
IRS-1B LISS-II / 6.3.1993
- for rabi season

Topography: gentle slope

Annual rainfall average: 446 mm

Major crops & duration (days) of total growing period

Kharif

Rabi

Guar 115

Wheat 135

Bajra 90

Mustard 145

Method applied

For each of the 17 minors of Mahendragarh distributary, crop acreage is estimated from the IRS-1B LISS-II satellite image-derived irrigation command land use-land cover and crop classification maps for both the rainy and the winter crop seasons, known in India as kharif and rabi. Following FAO guidelines, crop coefficient factors (Kc) are selected for each of four main crops and their monthly water requirements are calculated based on crop consumptive use (ET mm/d) multiplied by Kc (per month). The monthly net irrigation requirement for each of the four main crops is calculated. The monthly and seasonal net irrigation water requirements for each canal minor are then arrived at by multiplying monthly net irrigation water requirements with satellite data-derived crop acreage. The irrigation efficiency of a canal system depends on the type of channel, material used and its discharge. Since all the canals are lined, canal delivery efficiency is taken as 0.93 and the field channel efficiency as 0.80. Field data of the irrigation water supply (canal and tube well) and satellite data-based net irrigation water requirements are used to arrive at the net irrigation water deficit or surplus in each of the canal minor command areas in both kharif and rabi seasons of the year 1992-1993 (see Table 1 for the kharif season as a typical example).

Result

This study indicates that there exists deficiency of water for irrigation in all minors but four during the kharif season and five during the rabi season. Water deficiency varies from 6 to 57 percent of total crop water requirement during the kharif season and 0.7 to 48 percent during the rabi season. As an illustration, the irrigation water requirement and canal supplies of the Deroli minor during kharif and rabi seasons are shown in Figures 1a and 1b. The data obviously indicates the necessity of more canal supplies. Total crop water requirement, canal supplies and tube-well supplies (seasonal and yearly) are shown in Figure 1c. It is seen that crop water requirements are mainly met with the tube-well supplies only. The canal supply is very modest. However, few canal minors have adequate water supply during both seasons, due to extensive tube-well irrigation in these areas.

Conclusion

The average agreement between satellite-derived crop acreage and ground information (government records) is of the order of -7.8 percent to + 10.6 percent. The net irrigation water requirement estimation from satellite data, when compared with irrigation water supplies (canal and tube well), shows large-scale deficiencies, which will ultimately affect the crop yield. Crop yield estimation, which also can be done using satellite data through the normalized difference vegetation index values of crops and field information of CCE data, would validate the effect of water deficiencies on crop yield at de-aggregated level across the irrigation command.

References

Dastane N. G. 1975. Effective rainfall in agriculture. Irrigation & Drainage paper No24, FAO, Rome, 64 pp

Doorenbos J and Puritt W.O. 1977. Guidelines for predicting crop water requirements. Irrigation & Drainage paper No24, FAO, Rome

Food and Agriculture Organization. Irrigation water management training manual No3

Ministry of Irrigation, Government of India. 1984. A guide for estimating irrigation water requirements. Technical series (revised). Water Management Division, New Delhi, 144 pp

Prasad, V.H., Chakraborti, A.K. & Nayak, T.R. 1996. Irrigation command area inventory and assessment of water requirements using IRS-1B satellite data, Journal of Indian society of remote sensing, Vol24, No2, p 85-96

Table 1. Assessment of net irrigation water deficit/surplus during kharif season in Mahendragarh district in Haryana, India

Sl.No

Name of minor

July

August

September

October

Total kharif season

Deficit/Surplus (-) (+)

   

MWR

MCS

MWR

MCS

MWR

MCS

MWR

MCS

KWR

KCS

KWS

Ha-m

%

1

Lawan

38.297

9.716

8.484

0.719

138.958

0.000

114.808

7.356

300.548

17.791

198.778

-83.98

-27.9

2

Jhuk

21.045

0.211

4.662

0.000

67.690

0.000

49.952

0.000

143.350

0.211

121.323

-21.82

-15.2

3

Bucholi

16.132

9.306

3.574

0.000

42.482

0.000

26.869

16.774

90.057

26.080

108.300

45.32

50.9

4

Dewas

7.937

5.793

1.758

0.000

42.236

0.000

42.401

18.916

94.332

24.709

80.196

10.57

11.2

5

Bhandor

26.820

2.394

5.942

0.000

84.843

0.000

61.681

9.102

179.286

11.496

106.929

-60.86

-33.9

6

Deroli

9.075

1.593

2.010

0.000

24.880

0.000

15.007

4.187

50.973

5.780

26.047

-19.15

-37.6

7

Dholi

28.245

0.000

6.257

0.000

70.753

0.000

41.775

0.000

147.030

0.000

63.746

-83.28

-56.6

8

Sisot

29.387

2.185

6.511

0.000

102.645

0.000

81.090

1.893

219.632

4.078

131.604

-83.95

-38.2

9

Zerpur

31.666

4.187

7.015

0.000

73.279

0.000

36.196

3.641

148.156

7.828

74.028

-66.30

-44.8

10

Khatodra

20.118

1.365

4.457

0.000

57.825

0.000

38.474

1.183

120.874

2.549

80.882

-37.44

-31.0

11

Khaira

13.687

2.185

3.032

0.000

34.149

0.000

18.176

1.893

69.045

4.078

53.464

-11.50

-16.7

12

Jatwas

22.966

1.930

5.088

0.000

80.282

0.000

63.200

1.675

171.536

3.605

156.280

-11.65

-6.8

13

Nimbhera

12.943

0.000

2.867

0.000

54.839

0.000

48.732

0.000

119.382

0.000

98.703

-20.68

-17.3

14

CCI

12.134

0.342

2.688

0.000

40.187

0.000

30.512

0.000

85.520

0.342

85.680

0.50

0.6

15

Jonawas

19.517

0.291

4.324

0.000

55.255

0.000

38.375

0.255

117.470

0.546

88.422

-28.50

-24.3

16

Nihlawas

10.797

0.328

2.392

0.000

33.662

0.000

24.432

0.291

71.282

0.619

66.488

-4.18

-5.9

17

CC2

20.333

0.380

4.505

0.000

61.107

0.000

44.496

0.000

130.441

0.380

136.403

6.34

4.9



Satellite data-derived information

Irrigation water supply information:

   

MWR: Monthly irrigation water requirement (Ha-m)

MCS: Monthly supply of irrigation water through canals (Ha-m)

KWR: Kharif season total irrigation water requirement (Ha-m)

KCS : Kharif season irrigation water through canal (Ha-m)

 

KWS : Kharif season irrigation water from tube wells (Ha-m)

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