dc.description.abstract |
Soil quality is very much affected by land use and also soil depth. A study was
conducted at Sumbe sub-watershed, located in the Toke Kutaye District of West Showa
Zone of Oromia region, with the objective of evaluation of selected soil
physicochemical properties under different land uses and soil depth. The results
revealed the existence of spatial variation in soil properties among land use types and
with soil depth in a given land use. Relatively higher silt content (47.50%) was
recorded in the cultivated land soils, while clay was high (45.00%) in the forest and
grazing land soils followed by the cultivated land (32.25%). Higher bulk density
value (1.69 gcm-3) was recorded in the cultivated land soils followed by the 40-60 cm
layer of the forest (1.26 gcm-3) and grazing (1.25 gcm-3) soils. Relatively higher total
porosity value (62.3%) was recorded in the surface layer of the forest land soil
followed by the cultivated (57.7%) and grazing lands (54.7%). Soil pH ranged from
4.94 in the surface layer of the cultivated land soil to 6.74 in the 40-60 cm layer of the
forest land soils. The OM content ranged from 1.28% at the bottom layer of the
cultivated land to 8.49% at the surface layer of the forest land soils, whilst the total
nitrogen varied between 0.06% at the extreme bottom layer of the cultivated land to
0.42% at the surface layer of the forest land. Available phosphorus ranged from 2.00
mk kg-1 at the 40-60 cm layers of the cultivated and forest land soils to 6.40 mg kg-1 in
the surface layer of the grazing land. Relatively higher (8.35 Cmol(+)kg-1)
exchangeable Ca was recorded in soils of the forest land followed by the grazing and
cultivated land soils, whereas exchangeable Mg ranged from 2.21 Cmol(+)kg-1 at the
surface layer of the grazing land soil to 4.78 Cmol(+)kg-1 at the 40-60 cm layer of the
forest land soil. Similarly, exchangeable K ranged from 0.46 Cmol(+)kg-1 at the 20-40
cm layer of grazing land to 1.10 Cmol(+)kg-1 at the extreme bottom (40-60 cm) layer
of the forest land, while Na varied from 0.37 Cmol(+)kg-1 in the forest land soils to
0.57 Cmol(+)kg-1 at the 40-60 cm layer of the grazing land soil. PBS increased with
xiv
soil depth in all the land uses and varied between 33.8% at the surface layer of the
grazing land to 69.6% at the 40-60 cm layer of the forest land soils. Cu ranged from
0.11 mg kg-1 at the extreme bottom layer of the grazing land to 0.46 mg kg-1 at the
surface layer of the forest land soil. Iron varied from 10.68 mg kg-1 at the extreme
bottom layer of forest land soil to 30.63 mg kg-1 at the surface layer of the grazing
land. Fe varied from 10.68 mg kg-1 at the extreme bottom layer of forest land soil to
30.63 mg kg-1 at the surface layer of the grazing land. Mn ranged between 51.55 mg
kg-1 at the bottom layer of the grazing land soil to 80.63 mg kg-1 at the surface layer
soils in the same land use. Zn also ranged from 2.74 mg kg-1 at the 40-60 cm layer of
the cultivated land to 11.78 mg kg-1 at the surface layer soils of the same land use. The
soil attributes under the cultivated land showed an overall change towards the
direction of loss of its fertility compared to the adjacent forest land soils. Generally,
the values show that the overall soil condition in the cultivated and grazing lands is
deteriorating. |
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