Fjölrit RALA - 05.12.1999, Qupperneq 80

Fjölrit RALA - 05.12.1999, Qupperneq 80
78 Desertification in Ethiopian highlands Table 2. Annual soil movement (loss) documented in Ethiopia under various land use systems and topographic features (Hawando 1995). Land area Documented range of annual soil loss, ton/ha/year Land use type million ha 16 50 100 200 300 Annual soil movement, million tons 1. Cultivated land 18 288 900 1800 3600 5400 2. Pasture & rangelands 60 960 3000 6000 12000 18000 Total 78 1248 3900 7800 15600 23400 In the dryland areas in Ethiopia, 30.9 million ha, consisting of twenty five major soil great groups, are shallower than 50 cm. Further erosion will cause severe damage if rehabilitation measures are not taken in time. Out of the 30.9 million ha, 20.2 mil- lion ha occur in areas with xeric SMR, 5.2 million ha in aridic SMR and 4.6 million ha occur in ustic SMR zones (Hawando 1995). Soil conservation research project (SCRP; Humi 1988) and National Conservation Secre- tariat (1992) claim that soil losses may have been severely over-estimated by FAO (1984). The fig- ures for the soil loss by erosion from 6 SCRP sites range from 18-214.8 tons per ha per year (Table 3). When the soil loss figures obtained from SCRP sites are used to calculate the magnitude of soil loss from cultivated fíelds, pasture and rangelands, the amount of annual local soil movement ranges from 1,248-23,400 million tons per year (Table 2). It is reasonable to state that the soil movement fígures reported by FAO (1984) were not over-estimated. Rather, the figures estimated by National Conservation Se- cretariate and the Soil Conservation Research Project can be considered to grossly un- der-estimate the magnitude of land degradation in Ethiopia mainly because of low land area figures used in their calculations. Study by Lund University Geography Group (Helden 1987) concluded that land cover is the most important factor control- ling soil erosion, while precipitation characteristics and slope are also important. Therefore, for conservation and rehabilitation programme, we have to make sure that land cover is given the top priority. LOSS OF PLANT NUTRIENTS Associated with the soil movement is the loss of organic matter, nitrogen, phosphorus, potassium and other essential plant nutrients. Data in Table 4 shows that organic mat- ter loss associated with the removal of surface soil ranges from 15-1000 kg/ha/year which amounts to 1.17-78 million tons of organic matter lost per year from 78 million ha of cultivated and grazing lands. The loss of soil nitrogen ranged from 0.39-5.07 million tons per year and that of phosphorus ranged from 1.17-11.7 million tons per Table3. Soil erosion loss on 6 SCRP sites in various parts of Ethiopia (World Aragaye Berehe 1996). Site Soil loss (tons/ha/year) South Wollo 36.5-53.8 Sidamo 41.2-49.5 Harar 25.5-27.8 North Showa 152.4-214.8 Gojam 40.2-199.2 Illubabur 18.0-135.3
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