Abstract
Various woody species are growing in diverse landscapes and form a prominent component of farmland in Ethiopia. Farmers' preferences for woody species also vary in different parts of the country. The diversity and farmers' preferences for woody species have been described earlier. However, a simultaneous analysis of land use diversity and farmers’ preferences for woody species is scarcely available. Therefore, to fill the gap, this study was conducted in three selected highlands of Ethiopia to assess the land use diversity and farmers' preferences for woody species. A total of 320 households were randomly selected, and out of these, 105 households were purposely selected for species inventory. Overall, 525 plots were made using a 30 m × 30 m plot size for different land uses. Focus group discussion and key informant interviews were used for farmers’ preferences. The results imply that 32 woody species belonging to 16 families were recognized. Fabaceae was the leading family with 25% of species, followed by Rosaceae with 12.5% of species. In terms of species diversity, home garden (2.39) was more diverse than grazing land (1.94), crop land (1.50), boundary (0.92), and woodlot (0.54) in all areas. Among the preferred species, Eucalyptus globulus, Cuppressus lusitanica, Malus domestica, Cytisus proliferus, and Acacia decurrens were the most preferred and planted woody species by farmers. Generally, farmland maintains various tree and shrub species according to landscape practices. Farmers preferred and planted different woody species based on their benefits. Woody species must be maintained on farmland to overcome socio-economic and environmental problems.
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Acknowledgements
First, we would like to give our great thanks to our Almighty God for helping us in all our life. Also, we would like to express our deepest gratitude to Getinat Seyid and Hailu Belay for their unreserved guidance and encouragement. Our thanks go to Dagim Amare, Marshet Nigatu, Bayisa Kebede, Shibiru Gudeta, and Bogale Raya, who helped us during data collection. Special thanks go to the SIDA project program, the Ethiopian Environment and Forest Research Institute, and the Jimma Environment and Forest Research Center for the financial assistance and material support. Our thanks also go to the Environmental Protection, Forestry, and Climate Change Offices of Sinan, Welmera, and Yem woreda for giving us the essential data about study areas. We are also grateful to Tach Chabi, Welmera Choge, and Shewsher Almama kebele administrators and farmers for their endless provision during data collection.
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Appendices
Appendix
Appendix 1: List of trees and shrubs species found in the study areas
No | Scientific name | Family name | Origin | Type |
---|---|---|---|---|
1 | Acacia abyssinica | Fabaceae | Indigenous | Tree |
2 | Acacia decurrens | Fabaceae | Exotic | Tree |
3 | Acacia melanoxylon | Fabaceae | Exotic | Tree |
4 | Azadirachta indica | Meliaceae | Exotic | Tree |
5 | Cytisus proliferous | Fabaceae | Exotic | Shrub |
6 | Cordia africana | Boraginaceae | Indigenous | Tree |
7 | Croton macrostachyus | Euphorbiaceae | Indigenous | Tree |
8 | Cuppressus lusitanica | Cupressaceae | Exotic | Tree |
9 | Dombeya torrida | Sterculiaceae | Indigenous | Tree |
10 | Ekebergia capensis | Meliaceae | Indigenous | Tree |
11 | Erythrina abyssinica | Fabaceae | Indigenous | Tree |
12 | Erythrina brucei | Fabaceae | Indigenous | Tree |
13 | Eucalyptus globulus | Myrtaceae | Exotic | Tree |
14 | Eucalyptus camaldulensis | Myrtaceae | Exotic | Tree |
15 | Ficus sur | Moraceae | Indigenous | Tree |
16 | Grevillea robusta | Proteaceae | Exotic | Tree |
17 | Hagenia abyssinica | Rosaceae | Indigenous | Tree |
18 | Juniperus procera | Cupressaceae | Indigenous | Tree |
19 | Malus domestica | Rosaceae | Exotic | Tree |
20 | Millettia ferruginea | Fabaceae | Indigenous | Tree |
21 | Morus alba | Moraceae | Exotic | Tree |
22 | Olea europaea | Olacaceae | Indigenous | Tree |
23 | Persea americana | Lauraceae | Exotic | Tree |
24 | Podocarpus falcatus | Podocarpaceae | Indigenous | Tree |
25 | Prunus domestica | Rosaceae | Exotic | Tree |
26 | Rhus glutinosa | Anacardiaceae | Indigenous | Shrub |
27 | Rhus natalensis | Anacardiaceae | Indigenous | Shrub |
28 | Ricinus communis | Euphorbiaceae | Indigenous | Shrub |
29 | Rosa abyssinica | Rosaceae | Indigenous | Shrub |
30 | Sesbania sesban | Fabaceae | Indigenous | Shrub |
31 | Vernonia amygdalina | Asteraceae | Indigenous | Shrub |
32 | Yushania alpina | Poaceae | Indigenous | Woody grass |
Appendix 2: Importance value index of woody species in five land use types
Important value index of species | |||||||
---|---|---|---|---|---|---|---|
No | Species name | Land use categories | Average IVI | ||||
HG | BD | WL | CL | GL | |||
1 | Eucalyptus globulus | 47.03 | 146.7 | 197.5 | – | – | 78.26 |
2 | Cytisus proliferous | – | 6.86 | 4.15 | 118.0 | 35.94 | 32.99 |
3 | Cuppressus lusitanica | 63.50 | 59.11 | 35.45 | 4.52 | – | 32.51 |
4 | Acacia decurrens | 20.41 | 8.47 | 5.98 | 56.54 | 46.52 | 27.59 |
5 | Juniperus procera | 8.07 | 21.99 | – | 3.46 | 73.18 | 21.34 |
6 | Yushania alpina | 13.64 | 15.97 | 48.77 | – | – | 15.68 |
7 | Erythrina brucei | 4.30 | 3.98 | – | 33.48 | 27.35 | 13.82 |
8 | Vernonia amygdalina | 12.55 | 4.31 | – | 24.51 | 18.81 | 12.04 |
9 | Ficus sur | 2.78 | 2.18 | – | 14.84 | 26.64 | 9.29 |
10 | Acacia abyssinica | – | 2.18 | – | 9.39 | 32.32 | 8.78 |
11 | Malus domestica | 28.51 | – | – | 8.55 | – | 7.41 |
12 | Eucalyptus camaldulensis | 1.02 | 13.63 | 8.11 | – | – | 4.55 |
13 | Prunus domestica | 22.12 | – | – | – | – | 4.42 |
14 | Persea americana | 18.69 | – | – | – | – | 3.74 |
15 | Erythrina abyssinica | 1.02 | 3.73 | – | – | 13.05 | 3.56 |
16 | Grevillea robusta | 15.16 | 2.18 | – | – | – | 3.47 |
17 | Cordia africana | 1.72 | – | – | 10.43 | 3.86 | 3.20 |
18 | Ekebergia capensis | – | – | – | 5.87 | 8.45 | 2.86 |
19 | Croton macrostachyus | 3.97 | – | – | 3.46 | 3.86 | 2.26 |
20 | Hagenia abyssinica | 1.02 | 2.88 | – | – | 6.16 | 2.01 |
21 | Olea europaea | 2.11 | – | – | 3.46 | 3.86 | 1.89 |
22 | Sesbania sesban | 7.66 | – | – | – | – | 1.53 |
23 | Rhus glutinosa | 7.33 | – | – | – | – | 1.47 |
24 | Acacia melanoxylon | 6.51 | – | – | – | – | 1.30 |
25 | Millettia ferruginea | – | – | – | 3.46 | – | 0.69 |
26 | Dombeya torrida | – | 3.34 | – | – | – | 0.67 |
27 | Podocarpus falcatus | 3.29 | – | – | – | – | 0.66 |
28 | Azadirachta indica | – | 2.49 | – | – | – | 0.50 |
29 | Ricinus communis | 2.48 | – | – | – | – | 0.50 |
30 | Rhus natalensis | 2.11 | – | – | – | – | 0.42 |
31 | Morus alba | 1.99 | – | – | – | – | 0.40 |
32 | Rosa abyssinica | 1.02 | – | – | – | – | 0.20 |
Total | 300 | 300 | 300 | 300 | 300 | 300 |
HG-Homegarden BD-Boundary planting WL-Woodlot CL-Crop land GL-Grazing land.
Appendix 3: The lists of recorded species in decreasing order of basal area
Basal area of species in (m2/ha) | |||||||
---|---|---|---|---|---|---|---|
No | Species name | Land use categories | Total BA | ||||
HG | BD | WL | CL | GL | |||
1 | Eucalyptus globulus | 4.17 | 33.72 | 14.02 | – | – | 51.91 |
2 | Cuppressus lusitanica | 1.25 | 8.21 | 16.29 | 0.05 | – | 25.81 |
3 | Eucalyptus camaldulensis | 0.03 | 12.61 | 3.89 | – | – | 16.54 |
4 | Ficus sur | 1.67 | 5.34 | – | 0.67 | 1.49 | 9.17 |
5 | Yushania alpina | 0.60 | 1.97 | 5.32 | – | – | 7.88 |
6 | Juniperus procera | 0.39 | 3.68 | – | 0.06 | 2.33 | 6.46 |
7 | Acacia decurrens | 0.28 | 2.31 | 0.85 | 0.32 | 0.61 | 4.37 |
8 | Croton macrostachyus | 2.15 | – | – | 0.31 | 1.07 | 3.53 |
9 | Erythrina abyssinica | 0.15 | 1.71 | – | – | 1.26 | 3.12 |
10 | Cordia africana | 1.09 | – | – | 0.83 | 1.07 | 2.99 |
11 | Acacia abyssinica | – | 0.98 | – | 0.50 | 0.91 | 2.40 |
12 | Dombeya torrida | – | 2.05 | – | – | – | 2.05 |
13 | Grevillea robusta | 0.39 | 1.41 | – | – | – | 1.80 |
14 | Erythrina brucei | 0.36 | 0.89 | – | 0.14 | 0.31 | 1.70 |
15 | Vernonia amygdalina | 0.28 | 0.41 | – | 0.27 | 0.33 | 1.29 |
16 | Acacia melanoxylon | 0.80 | – | – | – | – | 0.80 |
17 | Cytisus proliferous - | 0.31 | 0.19 | 0.17 | 0.09 | 0.75 | |
18 | Olea europaea | 0.47 | – | – | 0.11 | 0.09 | 0.67 |
19 | Azadirachta indica | – | 0.63 | – | – | – | 0.63 |
20 | Persea americana | 0.63 | – | – | – | – | 0.63 |
21 | Hagenia abyssinica | 0.06 | 0.32 | – | – | 0.17 | 0.55 |
22 | Malus domestica | 0.27 | – | – | 0.13 | – | 0.40 |
23 | Ekebergia capensis | – | – | – | 0.13 | 0.25 | 0.38 |
24 | Podocarpus falcatus | 0.37 | – | – | – | – | 0.37 |
25 | Sesbania sesban | 0.14 | – | – | – | – | 0.14 |
26 | Rhus glutinosa | 0.14 | – | – | – | – | 0.14 |
27 | Prunus domestica | 0.08 | – | – | – | – | 0.08 |
28 | Ricinus communis | 0.07 | – | – | – | – | 0.07 |
29 | Millettia ferruginea | – | – | – | 0.06 | – | 0.06 |
30 | Rosa abyssinica | 0.04 | – | – | – | – | 0.04 |
31 | Rhus natalensis | 0.04 | – | – | – | – | 0.04 |
32 | Morus alba | 0.03 | – | – | – | – | 0.03 |
Total | 15.95 | 76.56 | 40.57 | 3.74 | 9.99 | 146.80 |
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Hailu, F., Derero, A. & Aticho, A. The impact of land uses on the diversity and farmers' preferences for woody species in the selected highlands of Ethiopia. Agroforest Syst (2024). https://doi.org/10.1007/s10457-024-00978-9
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DOI: https://doi.org/10.1007/s10457-024-00978-9