• Keine Ergebnisse gefunden

Land Degradation and Runoff Changes in the Highlands of Ethiopia

N/A
N/A
Protected

Academic year: 2022

Aktie "Land Degradation and Runoff Changes in the Highlands of Ethiopia"

Copied!
1
0
0

Wird geladen.... (Jetzt Volltext ansehen)

Volltext

(1)

! (

! (

!

( !(

! (

! (

! (

!

( !(

!

( !(

!

( !(

! (

!

! ( (

! (

!

( !(

! (

! (

! (

! (

Dese

Jinka

Selka

Jimma Ziway

Asela

Negele Awassa

Nazret Weliso

Gonder

Mekele

Gambela

Nekemte

Weldiya Bahr Dar

Dire Dawa

Arba Minch

Addis Abeba Debre Tabor

Mizan Teferi

Debre Birhan Debre Markos

0 75 150 300

km

Land Degradation and Runoff Changes in the Highlands of Ethiopia

Hans Hurni, Centre for Development and Environment (CDE), Switzerland; Berhanu Debele, NCCR North-South, Ethiopia; Gete Zeleke, Global Mountain Program, Ethiopia; Solomon Abate, Nile Basin Initiative, Ethiopia; Amare Bantider, Dilla University, Ethiopia; Birru

Yitaferu, Amhara Regional Agricultural Research Institute, Ethiopia; Eva Ludi, Overseas Development Institute, United Kingdom

The Ethiopian Highlands constitute 50% of the country and were once forested to a large extent.

Nowadays, merely 20% are covered by trees (3% by closed forest), evidencing a high extent of agricultural activities in the historic past and up to today. The consequences are land degrada- tion, and there is increased direct runoff in the highlands and to the lowlands.

Deforestation

Deforestation in Ethiopia has been a major land degradation process induced by farmers who wanted to change forest land for use as grassland and cropland. Most areas that currently have more than 3% tree cover are assumed to have been for- ested about 5000 years ago. Especially in the past millennium, the north-central highlands were a focus of agricultural expan- sion, where currently a 3-19% tree cover can be observed (cf.

Fig. 1). The zone with 19-40% canopy cover has been heavily deforested particularly in the past 50 years (cf. Fig. 3).

Soil degradation and runoff changes

Besides deforestation, soil erosion is a further process of land degradation. Agricultural activities and associated soil ero- sion have led to severe and widespread soil degradation. This is still threatening agricultural production despite a number of soil and water conservation measures introduced decades ago.

Land use change and advanced land degradation have also in- creased direct surface runoff (cf. Fig. 2), thereby benefitting lowland areas such as those in Sudan and Egypt, to which water is drained. With runoff the sedimentation rates also in- creased, posing problems for the reservoirs in the lowlands.

Figure 1: Present day tree and forest cover in Ethiopia as modified by agricultural activities during the last 5000 years (Hurni in prep.)

Figure 3: Intensive land cover and land use changes in Anjeni

Research Site near Debre Markos mainly occurred between 1950 and 1980 according to Gete Zeleke (2000) (Photo by H. Hurni 1984)

Conclusion

Land degradation remains a main threat to sustainable agricul- tural development, and the soils on slopes could be completely washed away within few generations. However, wise manage- ment of vegetation cover and soil structural measures have the potential to significantly reduce land degradation and improve agricultural production. Widespread application of these meas- ures has been, and must still be supported by government and the rural society.

Figure 2: Long-term runoff coefficients measured from testplot ex-

periments (2m by 15m) under natural rainfall and field conditions in seven research sites in the Ethiopian and Eritrean highlands between about 1981 and about 1996 (Hurni et al. 2005)

0 5 10 15 20 25 30 35 40 45 50

0 1 2 3 4 5

Andit Tid Anjeni Dizi

Gununo

Hunde Lafto Maybar

Afdeyu

Correlation 1: Forest; 2: Grassland; 3: Cultivated; 4: Degraded

Runoff in percent of rainfall

19 - 40 = open woodland (181,507km; 15.8%)

! (

Disclaimer

This map was composed by K. Hurni (CDE) using

MODIS Vegetation Continuous Fields data available at the Global Land Cover Facility (for more information see: http://glcf.umiacs.umd.edu/index.shtml).

Centre for Development and Environment, Institute of Geography, University of Bern.

Legend

Tree cover in percent per 500m x 500m pixel for 2001 (in brackets: area covered by class and in percentage of total country area)

0 - 3 = single trees in landscape (498,509km; 43.5%) 3 - 8 = scattered trees in landscape (138,909km; 12.1%) 8 - 19 = savannah-type landscape (232,356km; 20.3%) 40 - 70 = woodland (69,449km; 6.1%)

70 - 100 = forest land (17,665km; 1.5%)

Lakes and river water bodies (8,012km; 0.7%) Main towns

2 2

2 2

2

2

2

Referenzen

ÄHNLICHE DOKUMENTE

As Australia’s INDC does not report any projectons for the BAU scenario, our BAU and INDC mitgatons scenarios have been constructed based on the BAU scenario that was reported

• At the global level more than half of deforestation associated with agricultural products concerns the livestock sector dominated by pasture expansion for

Direct demand for land is the demand for land that is used directly for consumption of land, guided by market signals such as land prices and land rent regulating supply and demand

Observation of the distribution of land degradation by LU/LC patterns occurring in the forest zone of Russia clearly indicates that the degradation of forestland highly depends on

Various large-scale linear and nonlinear programming models have been used to simulate allocation of land between competing activities in agriculture and forestry,

Moreover, I will claim that agricultural land-use change is not only caused by increasing food demand due to population growth (as people usually assume), but also by

Unlike elsewhere, population in this region did not turn out to be an important factor in driving land use and land cover change (LULCC); however, it made its own contribution

they would know indicators of unsustainable land management, evaluate the importance of land problems (soil degradation) for instance on where and when degradation