Dessie Assefa Assefa’s research while affiliated with Bahir Dar University and other places

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Publications (1)


Figure 2: Long term average monthly rain fall, minimum, maximum and average temperature from 1994-2018 (Andit Tid metrological station), and 8 km far from the Tarmaber plantation forest)
Figure 3: Growing seeds from the soil seed bank (inside the glass house)
Figure 4: Species-area curve of all species in managed and unmanaged Tarmaber plantation forest and adjacent natural forest.
Figure 5: Frequency diagram of woody species in managed and unmanaged plantation forest and adjacent natural forests. A (natural forest), B (Managed C. Lusitanica), C (Not managed C. lusitanica), D (Managed E. globulus) and E (Not managed E. globulus)
Figure 6: Basal area of plantation forest with and without management intervention and adjacent natural forest

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Effects of Exotic Plantation Expansion and Management Intervention on Woody Plant Species Diversity, Regeneration and Soil Seed Bank in Tarmaber District, Ethiopia
  • Preprint
  • File available

January 2021

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180 Reads

Melese Bekele Nigussie

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Dessie Assefa Assefa

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Yohannis Gebremariam Gebremariam

This study was carried out in Tarmaber district north shewa zone Ethiopia to determine the effect of plantation forest with management intervention on woody plant species diversity, regeneration and soil seed bank species composition in five different forest types, which are adjacent natural forest, managed Cupressus lusitanica , unmanaged C. lusitanica , managed Eucalyptus globules and not managed E. globules plantation forests. A total of 75 circular sample plots of 314 m ² were established along a transect lines. Soil seed bank analysis was done from soil samples collected in each of the plots (225 samples) to examine the similarity between the soil seed bank and aboveground flora. Different diversity index and ANOVA was used in SPSS software for analysis. The result showed that a total of 51 woody plant species was recorded in adjacent natural forest (41), managed C. lusitanica (27), not managed C. lusitanica (9), managed E. globules (22) and not managed E. globules (13) species. Regeneration of seedlings were 3538, 5567, 707, 1462 and 2524 mean stems ha − 1 for natural forest, managed C. lusitanica , not managed C. lusitanica , managed E. globules and not managed E. globules respectively. Unmanaged C. lusitanica plantations had significantly lower densities of mature tree stems ha − 1 as compared to managed C. lusitanica , managed E. globules and adjacent natural forest (F = 14.03, p < 0.05).Similarly in terms of sapling density ha − 1 unmanaged C. lusitanica was significantly lower from other forest types (F = 7.37, p < 0.05). However managed C. lusitanica had significantly higher seedling regeneration (stem density ha − 1 ) than other plantation and adjacent natural forests (F = 16.11, p < 0.05). Generally mean stem densities including tree, sapling and seedling of woody species among different forest types managed C. lusitanica was significantly higher among different forest types (F = 13.01, p < 0.05). From the soil seed bank a total of 22 plant species (20 native and 2 exotic) species were recovered. In different forest types the number of species recorded was in adjacent natural forest (19), managed C. lusitanica (11), unmanaged C. lusitanica (4), managed E. globules (7) and unmanaged E. globules (5). The similarity of the oil seed bank was more or less similar to the above ground flora with maximum Sorenson’s similarity values of 0.633. Generally with appropriate management intervention undergrowth vegetation and soil seed bank status in plantation forest had good species composition and diversity.

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