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  • ACRS 1999


    Poster Session 5

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    Land Cover Change and its Effect on Runoff in the Doki River Catchment

    Ikuyo Makino* (Japan)
    * Rotech Co. Ltd.
    1403-1 Yahata, Chigasaki, Kanagawa 253-0085 JAPAN
    Phone & Fax: +81-467-85-5961
    Email: ikuyo@ff.iij4u.or.jp
    Susumu O
    gawa**, Genya Saito**

    **National Institute of Agro-Environmental Sciences
    3-1-1 Kannondai, Tsukuba, Ibaraki 305-8604 JAPAN
    Phone: +81-298-38-8192; Fax: +81-298-38-8199
    E-mail:remote@niaes.affrc.go.jp

    Keywords: agricultural fields, deforestation, evapotranspiration, Landsat TM, runoff ratio

    Abstract
    Land cover change and discharge fluctuation for the past 12 years in the Doki River catchment were examined using multi-temporal satellite data. This catchment is composed of mainly forest and some agricultural fields along the streams, the ratio of which is more than 10 % of the total area. Using the multi-temporal satellite data, Landsat TM, in 1986 and 1990, approximately 3 % of the total area had changed from forest to the agricultural fields during this period. From the water budget from 1981 to 1992 in the catchment, evapotranspiration decreased and runoff ratio increased. Short-term water budget led to monthly evapotranspiration before and after 1986, which showed the evapotranspiration in April and October decreased. Such change means agricultural activities, seeding and harvest. Moreover, statistical tests for hydrological data before and after 1986 showed that runoff ratio increased significantly with 0.05 of significant level. Therefore, one of the factors that caused the increase of runoff ratio in the catchment should be the land cover change from forest to agricultural fields.

    1. Introduction
    Land cover changes in the basin affect on its discharge and bring not only flood but also hard conditions to get agricultural and urban water supply. Especially, land use changes to agricultural fields or golf courses by deforestation have been paid attention as an important environmental change in the same way as urbanization recently (e.g. Jordan & Heuveldop, 1981). Then, land cover change and its effect on long-term water budget in the Doki river basin in the western part of Japan were examined from its satellite data and hydrological data. The effect of small development for land cover was evaluated with the long-term trends of water budget and the seasonal profiles of monthly evapotranspiration.

    2. Materials and Methods
    An objective site is located in the Doki river basin in Shikoku Island, Japan. The satellite data of multi-temporal Landsat TM (Table 1) were used for calculation of land cover classification, its area ratios, and NDVI.

    DEM, 25,000 and 50-m mesh, was used for the watershed separation. Hydrological data were precipitation and discharge in the Doki river observed for 12 years by Ministry of Construction. Discharge observation sites are located at Goyo Bridge (Drainage area: 72.1 km2 ) and Tsunekane Bridge (90.0 km2 ), while precipitation observation site is located at Miai at upper stream of the Doki river watershed as shown in Fig. 1. Meteorological data were used for evapotranspiration. The meteorological observation sites are at Tadotsu Meteorological Observation Station and Shikoku National Agricultural Experiment Station in Ministry of Agricultural, Forest and Fishery.

    Basin boundaries were determined semi-automatically by TNTmips, GIS software, from DEM with 50-m mesh. The boundary that intersects the discharge observation site was determined with geomorphologic maps considering micro drainage areas. Annual evapotranspiration was calculated from annual precipitation and discharge for 12 years in the Doki river basin using Equation (1). Water balance was calculated from monthly rainfall and discharge using the next equation to get evapotranspiration. Also runoff ratio was obtained from r=Q/P.


    where S is the storage, P the rainfall, Q the discharge, and E the evapotranspiration. Moreover, monthly evapotranspiration was also calculated with short-term water budget method.

    Daily evapotranspiration each land cover was derived from meteorological data using the Penman equation (Brutsaert, 1982).


    where D=(de*/dT)T, lº CpP/el, Qn is the available energy flux density in mm/day, f(u) the wind function in mm/day, u the mean wind speed in m/sec, ea* the saturation vapor pressure in hPa, ea the vapor pressure in hPa, Rn the net radiation in W/m2 , Ll the latent heat of vaporization (=2.454.106 J/kg), Rs the short-wave radiation in W/m2, as the albedo of the surface, Rld the downward long-wave radiation in W/m2 , Rlu the upward long-wave radiation in W/m2 , es the emissivity of the surface (=0.97), ea the atmospheric emissivity, a the Stefan-Boltzmann constant (=5.67*10-8Wm-2K-4), Ta the air temperature in K, and Ts is the surface temperature in K.Here, albedo each land cover was referred from empirical values (Kotoda, 1986).

    Land cover classification was carried out from Landsat TM with the maximum likelihood method to obtain 7 land covers: forest, paddy fields, vegetable fields, bare soils, urban areas and water body, and their area ratios. The ground truth was confirmed for land use in June 1998 and February and June 1999.


    Fig. 1 Doki River and its observation stations



    Table 1. Satellite data used. From 1986 till 1990, 
    agricultural development was carried out.
    Satellite Date
    LandsatTM 1986/4/12, 9/3, 11/6.1990/3/22, 5/9

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