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  • ACRS 1997


    Water Resources
    Subwatershed Prioritization for Watershed Management using Remote Sensing and GIS

    4.4. Prioritization Analysis
    As discussed earlier, the DSI, SI and PC were taken as the condition and used for the prioritization analysis by simple matrix method. To create this matrix, the range of quantitative value has been defined for qualitative value. Table 3 shows the qualitative for DSI, SI and PC.

    Table 3 Rating the Condition Indicator
    Rating DSI SI PC
    Very Low <1 - -
    Low 1 to 4 <0.1 <7
    Medium 4 to 6 0.1 to 0.5 7 to 15
    High 6 to 8 0.5 to 2 15 to 30
    Very High >8 >2 >30

    From the qualitative rating, the two-dimensional overlay matrix has been created by taking two indicators at a time. First the matrix analysis between DSI and SI had been done and they were grouped into 5 classes, which were used for second matrix analysis with PC. Lastly they were again grouped into five qualitative classes (Table 4). The group has been decided on the basis of the logical combination of the indicators. For example, the combination of high DSI and SI were grouped as first priority group. The output of the matrix analysis is given in Table 5, where all twenty-two subwatershed were classified in five group. Map 3 shows the spatial distribution of the subwatershed for conservation prioritization work.


    Map 3: Conservation Prioritization Map of the Trijuga Watershed, Nepal

    Table 4: Prioritization by Matrix Analysis with DSI, SI and PC.
    SI/DSI VL L M H VH   PC/DSI-SI VL L M H VH
    L 5 5 4 3 2 L 5 5 4 3 2
    M 5 4 3 2 2 M 5 4 3 2 2
    H 4 3 2 1 1 H 4 3 2 1 1
    VH 3 2 1 1 1 VH 3 2 1 1 1
    VL= Very Low, L=Low, M=Medium, =High, VH=Very high
    12,3,4 and 5 are the Priority Decreasing order

    Table 5: conservation Prioritization of the Subwatersheds
    Conservation Prioritization List of the subwathershed
    Fist Priority Chhaude-khola, Puwar-khola, Upper-Trijuga, Baruwa-Khola and Duwar-khola
    Second Priority Adheri-khola, Lava-khola, shahi-khola, Lalpatta-khola and Pharse-khola
    Third Priority Lower-Trijuga, Khajuri-khola and Bagha-khola
    Fourty Priority Hadiya-Khola
    Fifth Priority Deojor-khola, Kali-khola, thadi-khola, Khang-khola, Babiya-khola, Lohale-khola, Siwai-Naid and Ghiyar -khola


    5 Recommendations
    Conservation work in the Trijuga watershed area should be started according to the priority list of Table 5. Slope stabilization, slope failure protection, gully control by check dam, reforestation, growing of horticultural crop along with some other intensive soil conservation activities are required for the first ranking subwatersheds. Fifth ranking subwatershed need little attention like maintaining the crown cover and protection of the existing forest along with managed agriculture. Other subwatersheds should be treated by intermediate activities according to their ranks.

    6 Conclusion
    Delineating the wathershed area into subwatershed for priority based conservation work is essential and appropriate for the developing countries like Nepal. Considering its drainage system can do such delineation. The delineated subwatersheds were used for prioritization. Prioritization can be done by considering their forest loss, soil loss and land sensitivity, which is defined as the locational relationship between forest loss and soil loss. These factors were used to extract the DSI, SI and PC, which were considered as the condition indicator of the subwatershed. Using these condition indicators, a new method of prioritization for conservation work was proposed by the qualitative matrix analysis. Based on prioritization, subwatershed conservation management activities were proposed. Finally, it can be said that remote sensing and GIS in combination with USLE model can be used as appropriate tools for subwathershed prioritization.

    Reference
    • Aronoff, S. (1991), geographic Information systems: A Management Perspective, WDL Publications, Ottawa.
    • Burrough, PA.(1986), Principles of Geographic Information Systems for land Resources Assessment, Clarendon Press, Oxford.
    • DSCWM/HMG, Nepal (1992), Soil Conservation and Waterhsed management Operation Plan for Subwatershed of Palpa District, DSCWM/HMG, Nepal.
    • DSCWM (1983), Watershed Conditions of the districts of Nepal, Department of soil conservation and Watershed management, Kathmandu.
    • FAO (1985), Tropical Forestry Action Plan, Committee on Forest Development in the Tropics, FAO, UN, Rome.
    • Foster, G.R. (1988), modeling soil Erosion and Sediment Yield, In soil Erosion Research Methods, Editied by R. Lal ISSS, The netherland.
    • Lillesand, T.M. & Kiefer, R.W. (1987), Remote Sensing and Image Interpretation, John Wiley and Sons, New York.
    • Morgan, R.P.C. (1986), soil erosion and Conservation, Longman group UK Ltd., London.
    • Remote Sensing and GIS for Watershed Management, Asian-Pacific Remote Sensing Journal, Vol. 9, No. 2
    • Schawab, G.O., Fangmeier, D.D., Elliot, W.J. and R.K. Frevert (1993), Soil and Water conservation Engineering, 4th Edition, John wiley & Sons, Inc., NY.
    • Sharma, CK.(1981), Landslide and soil erosion in Nepal. 2nd Edition, Navana Printing Works Private Ltd., Calcutta.
    • Thapa, G.B. & K.E. Weber (1990), Managing Mountain Watersheds: The Upper Pokhara Valley, Nepal, HSD Monograph 22, AIT, Bangkok.
    • WEC (1982), Hydorlogical Studies of Nepal, Vol. I& II, WEC, Water and Energy Commission, Ministry of Water Resource, HMG, Nepal.
    • Wischmeier, W.H. and D.D. Smith (1978), Predicting Rainfall Erosion Losses A Guide to Conservation Planning, USDA Handbook 537, Washington.
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