Plant Community Composition and Structure of Asabot Dry Afromontane Forest, West Harare Zone, Ethiopia
Received Date: Oct 30, 2017 / Accepted Date: Dec 05, 2017 / Published Date: Dec 10, 2017
Dry Afromontane forests are the most altered and threatened ecosystem. Indeed, having a diverse ecosystem and biodiversity designated as a priority site in conservation. The objective of this study was to demonstrate plant community structure, regeneration status, and conservation priority species. The study was conducted on Asabot mountain forest which is found in West Harare Zone, Oromia National Regional State, Ethiopia. The vegetation sampling was designed at clustered altitude through mixed spatial stratified-random sampling method to ensure a full coverage of environmental variation and habitat heterogeneity. The main parameters used in vegetation characterization was diameter at breast height (DBH), height, seedling, and sapling of wood species recorded at sampled quadrat. The study analyzed plant community indicator species, importance value index, and vegetation structure and regeneration status, and conservation priority of selected species. The plant community was described by 97 species of 90 genera and 52 families. The result showed that eight specific trends and three general trends of population structure based on DBH, seedling, sapling and mature trees or shrubs. The dominant classes of the Asabot dry Afromontane forest were small trees and shrubs which is an indication of secondary vegetation. The conservation priority classification and visual field observations of some woody species were required urgent management intervention. Furthermore, the detail botanical aspects of the forest, the reason for the absence of regeneration in some tree species and socio-economic aspect of the vicinity is strongly recommended farther research in order to inaugurate appropriate management intervention.
Keywords: Dry afromontane forest; Plant community; Indicator species; Structural analysis; Regeneration status
The natural gifts of African countries with high endemism of animal and plant species passionate by Ethiopia diverse agroecology . The agricultural extensive and excessive deforestation hampered natural regeneration and seedling establishment that affected the diversity and structure of plant communities in most tropical forests [2-4]. In a similarly way forests in Ethiopia in general and dry Afromontane, in particular, have been affected by climatic and anthropogenic factors [5-9]. The assessment of forest cover change history of Ethiopia indicated reduction from 40% to less than 2.8% in the 19th century with current improvement to 15% [10,11]. The shifted vegetation shared half by Afromontane forest or mostly by dry Afromontane forests . The climatic characterization of Afromontane in Ethiopia distinguished by moisture than surrounding lowland [12,13]. The agroecology of dry Afromontane is described by an altitude range from 1500-3400 m above sea level; 700-1100 mm mean annual rainfall; and 14-25°C average annual temperature with coverage of distributed highland of central, northern, eastern and southern parts of Ethiopia [5,14,15]. This suitable for human inhabitation accompanied by sedentary agriculture, extensive cattle herding activities and socio-political instability. Dry Afromontane ecology exposed to heavy deforestation, forest fragmentation and loss of biodiversity, impoverishment ecosystems and climate change vulnerability . Indeed, they are a very important in-situ biodiversity conservation spot . In view, the study has been conducted valued on addressing plant community variation along an environmental gradient of Asabot mountain forest.
Though the current progress made on Asabot mountain forest demarcation as national wildlife protection sanctuary, the forest is currently continuously exploited by surrounding people for construction woodcutting, timber harvesting, charcoal production, firewood collection and other. Indeed, the plant community, floristic composition, and structure were not well studied yet. Therefore, the present study intended to analyze plant community, forest structure, and regeneration status of some woody species in order to forecast conservation priority and appropriate management.
Methods And Materials
Study site description
Asabot mountain forest is located in Miso district of West Harare Zone, Oromia Regional state, Ethiopia (Figure 1). Geographically, the study site is located at 40° 31’30 to 40° 42’0E and 9° 12’0 to 9° 21’0N. The altitude of Asabot Mountain ranges from 1087 to 2474 meters above sea level (Table 1).
|Altitude||Area in ha||Slope||Area in ha||Aspect||Area in ha|
Table 1: Description of Asabot mountain forest.
Asabot mountain forest is part of evergreen dry Afromontane ecology; characterized by average minimum (451.2 ml) and maximum (1055.5 ml) annual precipitation, mean minimum (11.9°C) and maximum (31.9°C) temperature, respectively according to metrological data for the last ten years (Figure 2).
The topography of the study site was raged mountain characterized by flat (1577 hectare) to rolling (803 hectares) (Table 1 and Figure 3). Asabot mountain ascends from 1080-2447 meter above sea level with immediate facing (aspect) change. However, the vegetation samples collected from an altitude range of 1778 to 2404 meter above sea level in order to reduce edge effects and due to the scope of the study.
The vegetation sampling method was chosen the mixed spatial stratified-random procedure to ensure a full coverage of environmental variation and habitat heterogeneity within the altitudinal gradient following Kent and Coker  and Muller-DuBois and Eilenberg . The direction of sampling quadrats was not followed strict procedure due to the complexity of the mountain. The quadrats covered clustered altitude of the study sites (lower, middle and upper) but aspect and slope not strictly followed. The 20 m × 20 m (400 m2) size sampling quadrats of 150 m and 100 m distance between transect and quadrat, respectively used. Inside the 20 m × 20 m quadrat five, 5 m × 5 m subplots, one at each corner and one at the center of the main quadrat were set to sample shrubs. The seedling and sapling data were collected from five 2 m × 2 m subplots, one at each corner and one at the center of the main plot. The diameter of all woody plants was recorded using diameter tape while height was measured using Hagan hypsometer and Clinometer. The diameter of normal individual trees was measured at breast height if the tree branched at breast height; and the diameter was measured separately and averaged if the tree was multi-stemmed. The diameter was measured individual and recorded if the tree buttressed at breast height. The diameter was also measured above or below the breast height at normal shape; and if the tree was angled or slopes, the diameter was measured opposite direction of the inclination (Figure 4).
Where topographic features made it difficult to measure trees and shrubs, height was estimated visually. The environmental variables such as altitude, slope, aspects and geographical coordinates were measured for each plots using Garmin Geographical Position System and satellite image . The specimens of all woody plant were pressed, dried and brought to the National Herbarium of Addis Ababa University for identification and storage. The wood plant nomenclature was followed Flora of Ethiopia and Eritrea book (FEE).
Plant community analysis
The dendrogram wood plant community cluster was analyzed based on cover abundance data of species composition in their hierarchical classification. The plant community types were named after two or three dominant species selected using the relative magnitude of their mean cover abundance values. The synoptic table classification indicator species of plant community in each particular cluster were produced using R statistical tool. Synoptic table produced from the summation of Relative density (RD)+Relative dominance (RDO)+Relative frequency (RF) in percent.
Importance value analysis
The importance value indices (IVI) were computed for dominant woody species based on their relative density (RD), relative dominance (RDO) and relative frequency (RF) as researcher Kenta and Coker described . Importance value index ( IVI)=Relative density (RD)+Relative dominance (RDO)+Relative frequency (RF), Where, Relative density (RD)=(number of individual’s species diameter at breast height (DBH) >2.5 cm)/(total number of individuals’) × 100, where, Relative dominance (RDO)=(Dominance of a species DBH>2.5 cm)/(Dominance of all species) × 100, where, Relative frequency (RF)=(Frequency of a species)/(Frequency of all species) × 100. However, the dominance is defined as the mean basal area per tree, multiplied by the number of trees of the species.
Structural data analysis
The DBH classes were analyzed based on the interval that class is, 1 stands for 1.0-2.50 cm, 2 stands for 2.51-10.0 cm, 3 stands for 10.01- 15.0 cm, 4 stands for 15.01-20.0 cm, 5 stands for 20.01-25 cm, 6 stands for 25.01-30.0 cm, and 7 stands for >30.0 cm. In the similar way height classes were analysed based on the intervals that class is1 stands for 2-5 cm, class 2 stands for 5.01-8 cm, class 3 stands for 8.01-12 cm, class 4 stands for 12.01-15 cm, class 5 stands for 15.01-20 cm and class 6 for more than 20.00 cm. As literature states basal area importance in providing a better measurement of the relative importance of the species than stem count , we analyzed basal area (BA) using a standard equation based on diameter at breast height. BA=d π2/4, where, BA is basal area, π=3.14; d is DBH (m). The density of trees or shrubs and basal area values were computed using a number of individuals per hectare and m2 per hectare, respectively. Furthermore, the vertical structure of the woody species was analyzed using the IUFRO classification scheme . This scheme categorizes a vertical structure of vegetation into upper, middle and lower story. The population structures of some selected species were also analyzed for the interpretation of the pattern of population dynamics in the forest.
Results And Discussions
Species composition: According to our sample, Asabot mountain forest was characterized by 103 species of 91 genera and 54 families. The trees species account for 26; shrubs species account for 36; lianas species account for 6 and 35 species were a woody hemi-parasite. Poaceae, Oleaceae, and Anacardiaceous were the most dominant families, contributing 12, 5 and 5 species to the total, respectively. These families were followed by Euphorbiaceous, Fabaceae, and Malvaceae which contribute four species while the remaining 46 families contributed only three and fewer species.
Plant community: The plant community analysis was clustered under three classes based on relative abundance of the individual in their respective samples (Figure 5). The clustering Euclidean distance was named after two dominant species within the group following Whittaker method . The abundance value of each species indicates the given community dominant species. The majority of sample plots have similar plant community abundance and classified under cluster one. Cluster 1 accounts for 54.14% sample plots; cluster 2 accounts for 31.43% sample plots; and cluster 3 accounts for 11.43% sample plots. The synoptic table indicated that the indicator species for plant community in cluster 1 were Olea europaea, Dodonea angustifolia, Pterolobium stellatum and Euclea racemose; cluster 2 plant community indicator species were Jasminum abyssinicum, Cuppuresses lusitanica, Maesa lanceolata, Rumex nepalensis and Terminalia catappa, and cluster 3 plant community indicator species were Teclea simplicifolia, Podocarpus falcatus, Grewia sp., Myrsine africana and Acokanthera schimperi. These species considered as Asabot dry Afromontane forest plant community indicator species and an illustration of species represents dry Afromontane forest ecology plant community if the macro and micro environmental variables variability not triggered. The plant community importance value index classes for each species showed an inverted J-shaped curve. That means most species in the first IVI class and few species in the last IVI class (Figure 6).
The synoptic table classification of plant community was represented indicator species in each cluster. Plant community indicator species in Cluster 1 were Olea europea, Dodonea angustifolia, Pterolobium stellatum and Euclea racemosa, and cluster 2 plant community indicator species were Jasminum abyssinicum, Cuppuresses lusitanica, Maesa Lanceolata, Rumex nepalensis and Terminalia catappa; cluster 3 plant community indicator species were Teclea simplicifolia, Podocarpus falcatus, Grewia sp., Myrsine africana and Acokanthera schimperi (Table 2). Those species were also considered as Asabot dry Afromontane forest plant community indicator species.
|Species||Cluster 1||Cluster 2||Cluster 3|
Table 2: Synoptic table cover-abundance values of species having higher value
Importance value index (IVI): Cuppuresses lusitanica, Olea europaea, and Podocarpus falcatus species had the highest importance value index (Table 3). This might be due to the contribution of endowed monastery community by protecting those high economic and cultural value species from the local intruders in demand of timber and other construction material. These three species contributed about 30.05% of the total importance values whereas the remaining woody species had combined IVI of about 69.95% (Table 3). Species with lower IVI need high conservation efforts while those with higher IVI need monitoring and management.
Table 3: Top ten species with high importance value index.
The study showed that most species have lower IVI classes whereas very few species have high IVI classes (Figure 6).
Tree and shrub density: The density of trees and shrubs with DBH greater than 1 cm was 875.97 individuals ha-1. The density of trees and shrubs with DBH 10-20 cm was 137.5 individuals ha-1. The density of trees and shrubs with DBH greater than 20 cm was 71.16 individuals·ha-1 (Table 4). The ratio described as c /d, is taken as the measure of size class distribution. Accordingly, the ratio of individuals with DBH 10.01-20 cm (c) to DBH >20 cm (d) was 1.93.
|DBH (cm)||No. of individuals (ha-1)||Percentage (%)|
Table 4: Density of trees and shrubs by diameter at breast height class.
The comparison of tree and shrub densities in DBH class 10.01-20 cm (c), DBH class greater than 20 cm (d) and C/D ratio for Asabot mountain forest with eleven other forests in Ethiopia were given in Table 5. The ratio of DBH 10-20 cm to DBH>20 cm at Asabot mountain forest was lower than Chi limo, Dindin, and Masha Andaracha, Menasha Suba, and Mena Angst forests but higher than Alata-Bolale, Woof Washi, Kamtok, Kamtok, Guar Freda, Donor and Doodle Forests (Table 5).
|Woof Washi||329.00||215.00||1.53||Bekele, 1993|
|Menasha Suba||484.00||208. 20||2.33||Bekele, 1993|
|Kamtok||330.00||215.00||1.53||Facade et al. 2012|
|Doodle||521.00||351.00||1.48||Hund era et al. 2007|
|Donor||526.00||285.00||1.85||Azalea et al. 2006|
|Guar Freda||500.00||263.00||1.90||Danu, 2006|
|Masha Andaracha||385.70||160.50||2.40||Yeshitelaet al. 2003|
|Dindin||437.00||219.00||2.00||Shibru and Balcha, 2004|
|Mena Angst||292.00||139.00||2.10||Lulekal, 2008|
Table 5: Comparisons of trees and shrubs density with DBH 10-20 cm (c) and tree density with DBH >20 cm (d) from Asabot mountain Forest with 11 other forests in Ethiopia.
DBH class distribution: The DBH class and wood species density showed the irregular relationship. As DBH increased from first class to second class, individual’s species number increased very high from 17.31stems ha-1 to 650 stems ha-1; then decreased and finally increased relatively. The curve was showed an irregular distribution of individuals across the DBH classes (Figure 7).
Tree species were classified according to different DBH classes, such as 1 stands for 1.0-2.50 cm, 2 stands for 2.51-10.0 cm, 3 stands for 10.01-15.0 cm, 4 stands for 15.01-20.0 cm, 5 stands for 20.01-25 cm, 6 stands for 25.01-30.0 cm, and 7 stands for DBH>30.0 cm. The DBH class distribution showed that more than 76% of all individuals had DBH less than 10.01 cm (Table 6).
|DBH Class||Density||Basal Area|
|Number of Stems||Percent (%)||Area (m2)||Percent (%)|
|Class 1||1.0 0-2.5||17.31||2.00||0.01||0.02|
Table 6: DBH class, Density and Basal Area of tree and shrub of asabot mountain evergreen natural forest.
Basal area: The mean total basal area of Asabot mountain forest is 22.45 m2 ha-1. The highest percentage of basal area (74.98%) contributed by DBH class 7 (DBH>30.0 cm), however, the DBH class of the rest individual tree density was contributed only 25.02%. Conversely, individuals in the DBH classes less than 30 cm had a density of about 95% of the total but accounted only 25.02% of the total basal area of the forest (Table 7 and Figure 8).
|Height Class||Density||Percent (%)|
|Class 1 2-5||512.5||58.50|
|Class 2 5.01-8||260.58||29.70|
|Class 3 8.01-12||53.85||6.10|
|Class 4 12.01-15||8.65||1.00|
|Class 5 15.01-20||8.65||1.00|
|Class 6 more than 20.00||31.73||3.60|
Table 7: Height class, density, and percent of trees and shrubs in the study site.
Species with the largest contribution in the basal area can be considered the most important woody species in the forest. Accordingly, descending order of some top tree species with the highest basal area in Asabot mountain forest was Podocarpus falcatus, Juniperus procera, Olea europaea, Olea welwitschii, Nicandra physaloides, Acacia abyssinica, Dodonea angustifolia, and Teclea nobilis.
The basal area of Asabot mountain forest was less than that of Wotagisho forest , Alata-Bolale Forest , Menasha Suba, Chilimo, and Denkoro Forests , Dindin Forests , Gendo Forest, Masha-Anderacha Forest , Jibat and Wof-Washa Forest .
Height class distributions: The density of individual trees and shrubs distribution along height classes of Asabot mountain forest were showed decreasing as height increases (Figure 9).
More than 88% of trees and shrubs were less than 8.01 m tall (Height classes 1 and 2). Only a small proportion, about 3.6%, reached a height of 20.01 m and above. The study showed that shorter plants were the dominant plant community (Table 7).
Vertical structure: The vertical structure story of Asabot mountain forest was classified using IUFRO classification scheme . The maximum tree’s height in Asabot mountain forest was 40 m which are comparable to another forest in Ethiopia. The main tree species that classified under upper story were Juniperus procera, Nicandra physaloides, Podocarpus falcatus, Euclea racemosa and Cassipourea malosana. When we compare each story based on the number of individual trees, the lower story was higher than the upper story (Table 8).
|Story||Height (m) Class||Stems||Species||Ratio of individuals to species|
|Density||Percentage (%)||No.||Percentage (%)|
Table 8: The vertical structure story of trees in the Asabot mountain forest.
The middle layer vertical structure of Asabot mountain forest was occupied by species including Capparis tomentosa, Cuppresus lustanica, Podocarpus falcatus, Olea welwitschii, Bersama abyssinica, Ficus Sur, and Olea europaea. However, the lower story was largely dominated by Acacia abyssinica, Acokanthera schimperi, Capparis tomentosa, Clerodendrum myricoides, Dodonea angustifolia, Euclea racemosa, Pavetta abyssinica, Ozoroa insignis, Protea gaguedi, Psydrax schimperiana, Rhus retinorrhoea, Schefflera abyssinica and Terminalia sp. The majority of species were concentrated in the lower story (76.27%) followed by the middle (15.25%) and very lowest at the upper story (8.48%) (Table 8). This showed a similar trend with Kamtok Afromontane moist forest  and Bonga Forest .
Plant diversity: Plant diversity indicates healthiness and survival capacity of ecology while unexpected environmental shocks happen. Species richness highest at cluster 1 (41.91%) and lowest at cluster 3 (18.38%). The Shannon diversity, Simpson diversity, Shannon Evenness and Simpson Evenness were highest at cluster 2 and lowest in cluster 3 (Table 9). Indeed, the study showed that high species richness not an indication of diversity and evenness.
|Cluster||Richness||Shannon diversity||Simpson diversity||Shannon Evenness||Simpson Evenness|
Table 9: Species richness, Shannon diversity index (H), Simpson diversity index, Shannon Evenness index (j) and Simpson Evenness index of each cluster.
The entire study site plant community structure was similar with cluster structure. The mean Shannon diversity index of plants in the study site was 1.61, Simpson diversity index was 4.83, Shannon Evenness index was 0.72 and Simpson Evenness index was 0.74 (Table 10).
|Berger Parker||Brillouin||Chao||D||Equitability||Evenness||Fisher alpha||Individuals||Margalef||Menhinick||H||Simpson||Taxa|
Table 10: Shannon Diversity index (H), Berger Parker, Brillouin, Chao, Dominance (D), Equitability, Evenness, Fisher alpha, Individuals, Margalef, Menhinick, H, Simpson, and Taxa.
Relative abundance, relative frequency, and relative dominance: Achyranthus aspera, Allium sp., Teclea simplicifolia, Celtis toka, Jasminum abyssinicum, Myrsine africana, Pittosporum Veridiflorum, Grewia sp. and Podocarpus falcatus were the most abundant species, account for 25.24% of total density. Olea europaea, Teclea simplicifolia, Achyranthes aspera, Euclea racemosa, Psydrax schimperiana, Acokanthera schimperi and Pterolobium were recorded highest frequency whereas Podocarpus falcatus, Cuppuresses lusitanica and Olea europaea were recorded highest relative dominance. Olea europaea, Cuppuresses lusitanica and Dodonea angustifolia were high relative frequency and high relative dominance species whereas Podocarpus falcatus and Achyranthus aspera were both high relative abundance and high relative dominance species. Indeed, Teclea simplicifolia was the only plant species with both high relative abundance and relative frequency in the study site (Table 11).
|Achyranthus aspera||5.81||Teclea simplicifolia||4.97||Podocarpus falcatus||44.67|
|Allium spalhaceum||3.18||Olea europaea||4.94||Cuppuresses lusitanica||25.38|
|Teclea simplicifolia||2.97||Euclea racemosa||4.27||Olea europaea||10.86|
|Celtis toka||2.64||Psydrax schimperiana||4.21||Olea welwitschii||2.54|
|Jasminum Abyssinicum||2.37||Acokanthera schimperi||3.6||Achyranthus aspera||1.76|
|Myrsine africana||2.12||Pavetta abyssinica||3.01||Acacia abyssinica||1.591|
|Pittosporum Veridiflorum||2.08||Dodonea angustifolia||2.78||Protea gaguedi||1.38|
|Grewia.sp||2.05||Juniperus procera||2.71||Dodonea angustifolia||1.28|
|Podocarpus falcatus||2.02||Cuppuresses lusitanica||2.65||Nicandra physalodes||1.2|
Table 11: Selected high relatively abundant, relatively dominant and relatively frequent species.
Population structure: The pattern of diameter class distribution indicates general trends of population dynamics and recruitment processes of each species. Indeed, the analysis of population structure for 27 species revealed eight specific and three general patterns (Figure 10). The total seedling, sapling, and mature woody tree densities of 27 selected species were about 1268, 231, and 911 individuals per hectare, respectively (Table 12). The structural analysis indicated the majority of plant community found in the DBH class 10 cm to 20 cm and the value less than most available studies in Ethiopia. But the ratio of medium (DBH class 10 to 20 cm) and large (DBH class >20 cm) was greater than Woof Washi , Kamtok , Doodle , Donor , Guar Freda , and Alata-Bolale  forests. The ration of medium and large classes was lower than Menasha Suba , Chilimo  and Masha Anderacha , Mena Angst  and Dindin . The plant community structure of Asabot dry Afromontane forest mainly represents by the two DBH classes if the microscale environmental variables variability not triggered.
Figure 10: Population structure of selected tree species (Tree species were classified according to different DBH classes, such as, 1 stands for 2.6-12.0 cm DBH, 2 stands for 12.1-22.0 cm DBH, 3 stands for 22.1-32.0 cm DBH, 4 stands for 32.1-42.0 cm DBH, 5 stands for 42.1-52.0 cm DBH, 6 stands for 52.1-62.0 cm DBH, 7 stands for >62.0cm DBH).
|Scientific name||Trees and shrubs||Saplings||Seedling||Sum of densities|
Table 12: Selected tree species with their seedling, sapling and mature tree density per hectare.
The DBH and height class distribution indicated an inverted J-shaped curve with most individuals in the lower size classes (Figures 7 and 8). However, the basal area class distribution of individuals showed J-shape. The DBH and height class distribution demonstrated a high rate of regeneration but the minimum number of tree density in the higher DBH and height class distribution might be due to the high rate of selective tinning. This agreed with studies conducted different parts of the country [1,33]. The total basal area of woody plant community in the sample plots of Asabot forest was 22.44 m2 ha-1. The highest basal area was contributed by Podocarpus falcatus, Juniperus procera, Olea welwitschii and Olea europaea. The predominance of these species in the forest was probably because of their spiritual significance and Asabot monastery community role in the management of forest from external intruders. But most of these species not dominate in another forest due to high market demand [1,33]. The study showed few plants contributed a large share of the total basal area confirming similar studies in Ethiopia [1,27,30,33].
The population of 27 selected tree species showed eight more specific and three general patterns based on DBH class of their abundance (Figure 9). Plant species represented their populations in particular pattern were Olea europaea, Dodonea angustifolia, Protea gaguedi, Acacia abyssinica, Juniperus procera, Podocarpus falcatus, Olea welwitschii and Conyza hypoleuca. Most of the pattern showed higher density in lower DBH classes which suggesting good reproduction and healthy regeneration potential. The other pattern showed the lowest density in the lower classes which is a sign of poor reproduction and recruitment. The other populations were represented by the irregular pattern. This result showed a similar trend with other studies in Ethiopia [1,24,34]. Most of the plant population in Asabot mountain forest was in a deficiency of intermediate DBH classes which might be due to selective removal of medium-sized wood plants. This might be due to Asabot mountain forest is the only natural forest in the vicinity currently under pressure of local intruders. In our observation, the main reasons for the absence of medium DBH classes were selective tinning for construction, timber and firewood.
Regeneration status of asabot mountain forest: The composition, distribution and density of seedlings and saplings are an indicator for the future habitat conditions, geographical distribution, composition, successful regeneration and survival and growth of forests within space and time [35-38]. The distribution of seedlings, saplings and mature trees/shrubs show eight distinct patterns and three general patterns (Figure 11).
Seven species (19.44%) were not represented by both seedlings and saplings, and only a few mature individuals were recorded for these species. On the other hand, five species (13.88%) of the total were not represented by saplings (Table 12). Accordingly, plant species were grouped into three conservation priority classes; Class 1 with no seedlings or saplings, Class 2 with seedlings but no saplings, and Class 3 with both seedlings and saplings greater than 1 individual’s ha-1 (Table 13).
|Class 1||Class 2||Class 3|
|Croton macrostachyus||Podocarpus falcatus||Calpurnia aurea|
|Ficus Sur||Sideroxylon oxyacanthum||Schefflera abyssinica|
|-||Clerodendrum myricoides||Cassipourea malosana|
|-||Acacia sp.||Capparis tomentosa|
|-||Bersama abyssinica Fresen.||Myrsine africana|
|-||Ozoroa insignis||Acokanthera schimperi|
|-||Protea gaguedi.||Juniperus procera|
|-||Acacia abyssinica||Terminalia catappa|
Table 13: Species conservation priority classes.
Plant species under conservation priority of class 1 and 2 might be due to human and cattle disturbance, grazing and browsing, seed predation, and the need of dormancy period for seeds of certain trees which causes insufficient seedlings and saplings. In addition, Facade and Coworker explained this phenomenon: litter accumulation, pathogens, moisture stress, and possession of alternative adaptations for propagation other than seed germination could also be the cause for lack of sufficient seedlings . This study showed a similar result with Gurmessa, et al. , Danu  and Simon and Grima . Indeed, our study showed plant species under conservation priority 1 and 2 might be under threat of local extinction and needs due attention.
Conclusion And Recommendation
The plant community in the study site within sampling quadrats was accounted for 103 species of 91 genera and 54 families. Dendrogram clustering of plant community based on their abundance was found more than 55% sample plots under similar class. The synoptic table which showed Olea europaea, Jasminum abyssinicum and Teclea simplicifolia was indicator species for their respective clusters and the study site. This illustrated Asabot dry Afromontane forest similar plant community abundance along the environmental gradient and structurally described by small trees and shrubs predominance was an indication of secondary regeneration forest type. The density of woody species inversely related with DBH and height classes implying good regeneration of the forest. The basal area of Asabot dry Afromontane forest covered by very few large plants while the majority contributed very small basal area. The population structure of Asabot mountain forest described by different patterns indicates high variation among species in population dynamics within the forest. The regeneration status analysis also showed that two species had no seedlings and saplings; seven species had no seedlings or saplings; and the rest species were represented by seedlings, saplings and trees or shrubs. The woody species of the Asabot dry Afromontane forest was classified into three priority classes for conservation based on their regeneration status giving due attention for first priority class as threatened species. Indeed, Asabot dry Afromontane forest is the only natural forest in the vicinity with high economic, social and political values for the local rural communities as a source of timber and non-timber forest products and ecosystem services for the lowland community. Indeed, the present multi-dimensional human influence on the natural forest needs urgent management strategy. Therefore, the first and the second priority class species should be given appropriate attention by all stakeholders. Furthermore, extensive research is needed to identify the reasons for the absence of regeneration in some species. In order to sustain forests, the vicinity participatory forest management programs should be introduced and implemented by sharing the responsibility of management and conservation with the local community through awareness creation and food security program. Finally, further investigation on the patterns of ecosystem functioning, socioeconomic and political environment in the vicinity should be studied for sustainable intervention.
- Gurmessa F, Soromessa T, Kelbessa E (2012) Structure and regeneration status of KamtokAfromontane moist forest, East Wollega Zone, west Ethiopia. J For Res 23: 205-216.
- Denslow JS (1980) Patterns of plant species diversity during succession under different disturbance regimes. Oecologia 46: 18-21.
- Runkle JR (1982) Patterns of disturbance in some old-growth mesic forests of eastern North America. Ecology 63: 1533-1546.
- Bussmann RW (2001) Succession and regeneration patterns of East African mountain forests. Systematic and Geography of Plants 71: 957-974.
- Friis I (1992) Forest and forest trees of northeast tropical Africa: their natural habitats and distribution pattern in Ethiopia, Djibouti and Somalia. Kew Bull Add Ser 15: 1-396.
- Machado JM, Perez-Gonzalez A, Benito G (1998)Paleoenvironmental changes during the last 4000 yr in the Tigray, northern Ethiopia. Quaternary Research 49: 312-321.
- Tekle K, Hedlund L (2000) Land cover changes between 1958 and 1986 in Kalu district, SouthernWello, Ethiopia. Mt Res Dev 20: 42-51.
- Zeleke G,Hurni H (2001) Implications of land use and land cover dynamics for mountain resource degradation in the northwestern Ethiopian highlands. Mt Res Dev 21: 184-191.
- Dessie G, Kleman J (2007) Pattern and magnitude of deforestation in the south central Rift Valley region of Ethiopia. Mt Res Dev 27: 162-168.
- Ethiopian Forest Action Program (1998) National Action program to combat Desertification. Addis Ababa: Environmental Protection Authority.
- Ethiopian Forest Action Program (1994) Ethiopian Forestry Action Program. The Challenge for Development. Addis Ababa: Ministry of Natural Resources 3: 138.
- Logan WEM (1946) An Introduction to the Forests of Central and Southern Ethiopia. Oxford: Imperial Forest Institute, UK, p: 38.
- Bekele T(1994) Phytosociology and Ecology of Humid Afromontane Forest on the Central plateau of Ethiopia. J Veg Sci 5: 87-98.
- Taketa D (1996) Seed Ecology and Regeneration in Dry Afromontane Forests of Ethiopia. Doctoral thesis, Swedish University of Agricultural Sciences, Umeå.
- Friis I, Demissew S, van Breugel P (2010) Atlas of the potential vegetation of Ethiopia.The Royal Danish Academy of Science and Letters, Copenhagen .Biologiske Skrifter, vol 58.
- Taketa D(2001) Deforestation, wood famine, and environmental degradation in Ethiopia’s highland ecosystems: urgent need for action. Northeast African Studies 8: 53-76
- Williams JW, ReVelle CS, Levin SA (2004) Using mathematical optimization models to design nature reserves. Front Ecol Environ 2: 98-105.
- Kent M, Coker P (1992) Vegetation Description and Analysis: A practical approach; New York: John Wiley and Sons, USA, p: 363.
- Muller-DuBois D, Eilenberg H (1974) Aims and Methods of Vegetation Ecology. New York: Wiley and Sons, USA, p: 547
- Cain SA, de Olivieria Castro GM (1959) Manual of Vegetation Analysis. Harper and Brothers Publishers, New York, USA, p: 325.
- Zanella A, Jabiol B, Ponge JF, Sartori G, De Waal R, et al. (2011) European Humus Forms Reference Base.
- Whittaker RH (1972) Evolution and measurement of species diversity. Taxon 21: 213-251.
- Unbushe D, Tekle T (2016) Floristic Composition and Diversity of Woody Plant Species of Wotagisho Forest, Boloso Sore Woreda, Wolaita Zone, Southwest, Ethiopia. Int J Nat Resour Ecol Manage 1: 63-70.
- Enkossa W (2008) Floristic analysis of Alata-Bolale Forest in GudayaBillaWoreda, East Wollega, Oromia Regional State, West Ethiopia (M.Sc. Thesis). Ethiopia: Addis Ababa University.
- Bekele T, Ayalew A, Demissew S (2006)The undifferentiated Afromontane forest of Denkoro in the central highl and of Ethiopia: A floristic and structural analysis. SINET: Ethiop J Sci 29: 45-56.
- Simon S, Girma B (2004) Composition, structure and regeneration status of woody species in Dindin Natural Forest, Southeast Ethiopia: An implication for conservation. Ethiop J Biol Sci 3: 15-35.
- Yeshitela K, Bekele T(2003) The woody species composition and structure of Masha Anderacha forest, Southwestern Ethiopia. Ethiop J Biol Sci 2: 31-48.
- Bekele T (1993) Studies on remnant Afromontane forests on the central plateau of Shewa, Ethiopia. ActaPhytogeographicaSuecicaPhytogeogr. Suec 79: 1-58.
- Soromessa T, Kelbessa E (2008) Interfaces of regeneration, structure, diversity and uses of some plant species in Bonga Forest: A reservoir for wild coffee gene pool. SINET: Ethiop J Sci 31: 121-134.
- Hundera K, Bekele T, Kelbessa E(2007) Floristic and phytogeographic synopsis of a dry afromontane coniferous forest in Bale Mountains, Ethiopia: Implication to biodiversity conservation. SINET: Ethiop J Sci 30: 1-12.
- Danu D (2006) Floristic Composition and Ecological Study of Bibita Forest (Guar Freda), Southwest Ethiopia, M.Sc. Thesis. Addis Ababa University. Ethiopia.
- Lulekal E, Kelbessa E, Bekele T, Yineger Y (2008) Plant species composition and structure of the Mana Angst moist montane forest, Southeastern Ethiopia. J E Afri Nat Hist 97: 165-185.
- HunderaK, Gadissa T (2008) Woody species composition and structure of the Belete Forest, Jimma Zone, SW Ethiopia, Ethiop J Biol Sci 7: 1-15.
- Senbeta F, Woldemariam T, Demissew S, Denich M (2007) Floristic diversity and composition of Sheko Forest, Southwest Ethiopia. Ethiop J Biol Sci 6: 11-32.
- Khumbongmayum AD, Khan ML, Tripathi RS (2005) Survival and growth of seedlings of a few tree species in the four sacred groves of Manipur, Northeast India. Current Science 88: 1781-1788.
- Henle K, Saree S, Wiegand K (2004) The role of density regulation in extinction processes and population viability analysis. Biol Conser 13: 9-52
- Grubb PJ (1977)The maintenance of species richness in plant communities. The importance of the regeneration niche. Biol Rev 52: 107-145.
- Good NF, Good RE (1972) Population dynamics of tree seedlings and saplings in mature.Eastern hardwood forest. Bulletin of Torrey Botanical Club 99: 172-178.
Citation: Tura TT, Soromessa T, Leta S, Argaw M (2017) Plant Community Composition and Structure of Asabot Dry Afromontane Forest, West Harare Zone, Ethiopia. J Biodivers Endanger Species 5: 202. doi: 10.4172/2332-2543.1000202 Doi: 10.4172/2332-2543.1000202
Copyright: ©2017 Tura TT, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Select your language of interest to view the total content in your interested language
Share This Article
- Total views: 722
- [From(publication date): 0-2017 - Jun 24, 2018]
- Breakdown by view type
- HTML page views: 625
- PDF downloads: 97