International Journal of Biodiversity
Volume 2016 (2016), Article ID 7930857, 8 pages
http://dx.doi.org/10.1155/2016/7930857

Research Article

Diversity of Woody Plant Species of Gamuwa and Oda Forests of Humbo Carbon Project, Wolaita, Ethiopia: For Conservation and Management of Forests

Markos Kuma

Department of Biology, Wolaita Sodo University, Wolaita Sodo, Ethiopia

Received 7 June 2016; Accepted 26 October 2016

Academic Editor: Alexandre Sebbenn

Copyright © 2016 Markos Kuma. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

This study was conducted in the Community Managed Forests of Gamuwa and Oda of Carbon Project of Humbo, Wolaita, Ethiopia. The objective of the study was to explore diversity of woody species for conservation and management of the forests. A total of 64 (20 m × 20 m) quadrats were sampled to gather data of species cover abundance, altitude, aspect, and slope. Vegetation clustering was performed from cover abundance using XLSTAT version 2015.2.03 software package. Similarity coefficient was computed using number of species that existed in each community and had been common to them. Diversity indices were computed from number of individuals of each species using Multivariate Variate Statistical Package (MVSP) version 3.1. The General Linear Model (GLM) analysis confirmed the presence of significant difference ( value = 0.001) of species distribution, altitude, and slope among the quadrates of the three community types. However, except aspect in community 3 ( value = 0.005) slope, aspect, land cover, and altitude insignificantly affected the distribution of species in communities. Therefore, a priori management and conservation should be given for families with only one species, community with high dominance (), and the area with less land cover.

1. Introduction

Background and Justification. The management of forest ecosystems can pay dividends in terms of water and nutrient availability and reversal of land degradation, having positive impacts on livelihoods and helping in poverty reduction [1, 2]. However, deforestation leads to degradation of the forest and is estimated to contribute globally to a further emission of around 0.5 Gt carbons per year into the atmosphere [3]. A pressure on forestlands of Ethiopia is due to rapid growth of human population [4, 5]. The anthropogenic activities will influence the vegetation dynamics and tree density at the local and regional scales [6], structure the plant communities of the area [7], determine the size class distribution of species [8], and lead to depletion of forest resources [9].

Botanical assessments are crucial in identifying plant diversity, protecting threatened and economic species, monitoring the status of reserves, and understanding the extent of plant diversity in forest ecosystems [10–12]. Hence, the vegetation analysis enables us to build a mental picture of an area under investigation, compare and ultimately classify communities of the vegetation [13], and understand the relationship that exists within communities and among their environments [14].

Even though the floristic composition, vegetation structure, and regeneration status of woody plant species of Oda forest have been studied [15], the requirement of diversity of woody plant species is not undertaken in the forests. Therefore this study was conducted to identify plant communities and analyze diversity of woody plant species in the forests. In addition to analysis of floristic composition and structure, such a kind of study is fundamental and crucial element for conservation and management of the forests.

2. Materials and Methods

2.1. Description of the Study Area

The study areas are located in SNNPR, Wolaita Zone, Humbo Woreda, Hobicha Bongota, and Bolla Wanche Kebeles. The sites are located about 410 to 430 km away from Addis Ababa (Figure 1). The vegetation of Gamuwa which is found in Bolla Wanche Kebele is positioned at latitude of 6°46′ and 6°45′N, longitude of 37°49′ and 37°50′E, and altitude ranges from 1708 to 1882 m a.s.l.

Figure 1: Map of study area (source: [15]).

The vegetation of Oda which is found in Bongota Kebele is situated at latitude of 6°44′, longitude of 37°52′ and 37°53′E, and altitude ranges from 1625 to 1929 m a.s.l. [15]. The Oda forest lies within the lowland agroecological zone but Gamuwa forest lies within midland agroecological zone [16].

2.2. Data Collection

The height of individuals of a species, land cover, and cover abundance of woody plant species were collected from each quadrate (20 m × 20 m). Altitude and coordinate points (using Magellan GPS 315 2001), slope degree (using Suunto Finland clinometers), and aspect (using Silver Type 2 compass) were measured for each quadrat.

The cover abundance data estimated from each quadrat was later converted into cover abundance values using modified 1–9 Braun-Blanquette scale [17]: 1 = rare (1–3 individuals), 2 = few individuals, ≤5%, 3 = abundant, ≤5%, 4 = very abundant, ≤5%, 5 = 5–12.5%, 6 = 12.6–25%, 7 = 25.1–50%, 8 = 50.1–75%, and 9 = >75% cover.

2.3. Data Analysis

2.3.1. Vegetation Data Analysis

The information recorded from all tree, shrub, and liana species from 64 quadrats was used for identification of plant community and for computation of diversity indices. Plant communities were identified by hierarchical cluster analysis (HCA) using XLSTAT version 2015 based on the cover abundance data of a species in a given quadrat.

Naming of plant communities was carried out after identification of two or three species with the highest mean cover abundance value in each cluster. Individuals having DBH <2.5 cm and height ≤0.6 m were counted as seedling whereas individuals with 2.5 cm ≤ DBH ≤ 15 cm and 0.61 ≤ height ≤ 3 m were counted as sapling [15].

2.3.2. Plant Diversity Analysis

Each community type was identified using mean cover abundance value of the species and the diversity of each cluster was calculated by Shannon-Weiner diversity index using the following formula:where is diversity of species; = the number of species; = the proportion of individuals abundance of the th species; and ln is .

Simpson index () and the evenness index ( = evenness) are used as a measure of species dominance and a measure for evenness of spread of species, respectively [18]:where is Simpson index, is the proportion of individuals abundance of the th species, and is summation.

As biodiversity increases, the Simpson index decreases. Therefore, compute to get a clear picture of species dominance of the community. .

The even spread of species in the community was calculated by the formula where is evenness of spread, is Shannon-Wiener diversity index, is the number of species, is ,  max is .

Floristic similarities among different quadrates and plant communities were calculated by employing Sörensen’s similarity coefficient [19] by using the following equation:where is Sörensen’s similarity coefficient, is number of species common to both samples, is number of species in sample 1, and is number of species in sample 2.

2.3.3. Environmental Data Analysis

Physiogeographical variables in accordance with the community type identified were computed using SPSS 20 version for their significant effect on species distribution among the plant communities of the forests.

3. Results

3.1. Families of the Forests

A total of 80 woody species belonging to 43 families were identified from the forests. Among the families of the area, 1 family of the forests (Fabaceae) was found to be the most dominant family and contributed 10 species to the forests (12.5%). Twenty-six families of the forests (Acanthaceae, Aloaceae, Anacardiaceae, Annonaceae, Apiaceae, Araliaceae, Bignoniaceae, Dracaenaceae, Ebenaceae, Ericaceae, Flacourtiaceae, Guttiferae, Hypericaceae, Lamiaceae, Melianthaceae, Olacaceae, Oliniaceae, Podocarpaceae, Rubiacea, Santalaceae, Solanaceae, Thymelaeaceae, Ulmaceae, Verbenaceae, and Vitaceae) were found to be the least dominant families and each of them contributed only one species to the forests (32.5%). But the remaining 16 families (Combretaceae, Oleaceae, Capparidaceae, Celastraceae, Euphorbiaceae, Moraceae, Myrtaceae, Rubiaceae, Sapindaceae, Tiliaceae, Apocynaceae, Asteraceae, Myrsinaceae, Proteaceae, Rhamnaceae, and Rutaceae) contributed 44 species to the forests (55%). Generally, the families of the forests contributed 45% of tree species, 52.5% of shrub species, and 2.5% of liana species.

3.2. Plant Community Types

Agglomerative hierarchical clustering (AHC) analysis identified three plant communities from the forests using cover abundance data. Twenty-nine quadrats were clustered in community type one, 15 quadrates were clustered in community type two, and 20 quadrats were clustered in community type three of the forests (Figure 2).

Figure 2: Dendrogram that shows community type of the forests (green = C1, pink = C2, and red = C3 = community type). Note: in the dendrogram a broken line marks that the level of truncation has been carried out and the dissimilarity level of the community.

3.2.1. Community 1: Syzygium guineense and Dodonaea angustifolia

Twenty-nine quadrats with 76 species clustered in this community type were distributed at average altitude of 1840 m a.s.l. and slope degree of 18. High mean cover abundance of this community was occupied by Syzygium guineense (7.24), Dodonaea angustifolia (6.03), Combretum molle (3.66), Terminalia schimperiana (3.48), Carissa edulis (3.21), and Euclea schimperi (3.17).

The zero mean cover abundance was occupied by Ocimum gratissimum, Pappea capensis, Piliostigma thonningii, Rytigynia neglecta, and Ximenia americana (Table 1). That means 5% of the species of the forest were not confined in this community.

Table 1: Mean cover abundance of Woody species.

Community type
1
2
3

Number of quadrats
29
15
20

Combretum molle R.Br. ex G.
3.66
4.8
6.55

Dodonaea angustifolia L.f.
6.03
5.93
5.8

Rhus natalensis Bernh. ex Krauss
0.55
3.47
5.1

Combretum collinum Fresen. spp. binderianum (Kotschy) Okofor
1.1
1.4
4.3

Schrebera alata (Hochst.) Welw.
1.62
2.6
3.7

Terminalia schimperiana Hochst.
3.48
3.2
1.95

Calpurnia aurea (Ait.) Benth.
0.86
2.33
1.9

Olea capensis L.
1.86
1.93
1.75

Acacia hockii De Wild.
0.21
0.67
1.6

Dichrostachys cinerea L.
2.41
0.8
1.5

Clutia abyssinica Jaub. & Spach
0.72
0.4
1.4

Carissa edulis L.
3.21
2.73
1.2

Allophylus abyssinicus (Hochst.) Radlk.
1.55
1.93
1.2

Grewia bicolor Juss.
0.14
0.47
1.15

Pterolobium stellatum (Forssk.) Brenan
0.17
1
0.95

Albizia schimperiana Oliv.
0.14
0.53
0.85

Jasminum floribundum R.Br. ex Fresen.
0.79
0.8
0.8

Ozoroa pulcherrima (Schweinf.) R. & A. Fernandes
0.1
0.4
0.75

Euclea schimperi (A.DC.) Dandy
3.17
8.27
0.6

Myrtus communis L.
1.03
1.8
0.6

Maerua oblongifolia (Forsk.) A. Rich.
0.24
0.13
0.6

Croton macrostachyus Hochst.
0.41
0.8
0.55

Rhoicissus revoilii Planch.
0.41
0.47
0.55

Markhamia lutea (Benth.) K.Schum.
0.72
0.87
0.5

Acokanthera schimperi (A.DC.) Schweinf.
0.9
2
0.45

Olea europaea L. ssp. cuspidata (Wall. ex G. Don) Cif.
1.69
3
0.4

Hypericum revolutum Vahl
2.14
1.2
0.4

Teclea nobilis Del.
0.21
0.07
0.4

Maytenus gracilipes (Welw. ex Oliv.) Exell
0.86
0.73
0.35

Vernonia karaguensis Oliv. & Hiern.
0.1
0.33
0.35

Flacourtia indica (Burm.f.) Merr.
0.21
0.2
0.35

Olinia rochetiana A. Juss.
1.34
2.07
0.3

Grewia velutina (Forssk.) Vahl
0.03
0.07
0.3

Capparis fascicularis DC.
0.07
0
0.3

Syzygium guineense (Willd.) DC.
7.24
0.93
0.25

Protea gaguedi J. F. Gmel.
1.34
0.8
0.25

Entada abyssinica Steud. ex A. Rich.
0.24
0.27
0.25

Ficus vasta Forssk.
0.03
0
0.25

Clutia lanceolata Forssk.
0.52
0.53
0.2

Maerua angolensis DC.
0.55
0.4
0.2

Osyris quadripartita Decn.
0.34
0.33
0.2

Piliostigma thonningii (Schumach.) Milne-Rodh.
0
0
0.2

Fagaropsis angolensis (Engl.) Milne-Redh.
0.07
0.27
0.15

Senna petersiana (Bolle) Lock
0.07
0
0.15

Rothmannia urcelliformis (Hiern) Robyns
0.66
0.87
0.1

Rhamnus prinoides L. Herit
0.34
0.4
0.1

Gnidia glauca (Fresen.) Gilg.
0.17
0.4
0.1

Maytenus senegalensis (Lam.) Exell
0.41
0.27
0.1

Sansevieria ehrenbergii Schweinfurt ex Baker
0.14
0.2
0.1

Crotalaria pallida L.
0.14
0.13
0.1

Garcinia buchananii Baker.
0.24
0
0.1

Ocimum gratissimum L.
0
0
0.1

Uvaria scheffleri Diels
1.41
1.4
0.05

Ficus ingens L.
0.03
0.73
0.05

Salacia congolensis De Wild. & Th. Dur.
0.28
0.33
0.05

Celtis africana Burm.f.
0.24
0.07
0.05

Acacia senegal (L.) Willd.
0.38
0
0.05

Bersama abyssinica Fresen.
0.1
0
0.05

Polyscias fulva (Hiern) Harms
0.07
0
0.05

Gardenia ternifolia Schumach.
0.03
0
0.05

Vernonia filigera Oliv. & Hiern.
0.03
0
0.05

Pappea capensis Eckl. & Zeyh.
0
0.27
0

Combretum aculeatum Vent
0.41
0.2
0

Tricalysia niamniamensis Heirn
0.31
0.13
0

Justicia adhatoda L.
0.07
0.13
0

Ximenia Americana L.
0
0.13
0

Myrsine africana L.
0.45
0.07
0

Steganotaenia araliacea Hochst. ex A. Rich
0.1
0.07
0

Solanum incanum L.
0.03
0.07
0

Rytigynia neglecta (Hiern) Robyns
0
0.07
0

Podocarpus falcatus (Thunb.)
0.21
0
0

Ficus sur Forsk
0.17
0
0

Eucalyptus camaldulensis Dehnh.
0.1
0
0

Aloe gilbertii Sebsebe & Brandham
0.07
0
0

Maesa lanceolata Forssk.
0.07
0
0

Erica arborea L.
0.03
0
0

Grevillea robusta R.Br.
0.03
0
0

Lippia adoensis Hochst. ex Walp.
0.03
0
0

Triumfetta brachyceras K. Schum.
0.03
0
0

Ziziphus mauritiana Lam.
0.03
0
0

3.2.2. Community 2: Euclea schimperi and Dodonaea angustifolia

Fifteen quadrats with 59 species clustered in this community were distributed at the average altitude of 1843 m a.s.l. and slope of 19. In this community Euclea schimperi (8.27), Dodonaea angustifolia (5.93), Combretum molle (4.8), Rhus natalensis (3.47), Terminalia schimperiana (3.2), and Olea europaea (3.0) were woody species with high mean cover abundance.

The species with zero mean cover abundance were Capparis fascicularis, Ficus vasta, Piliostigma thonningii, Senna petersiana, Garcinia buchananii, Ocimum gratissimum, Acacia senegal, Bersama abyssinica, Polyscias fulva, Gardenia ternifolia, Vernonia filigera, Podocarpus falcatus, Ficus sur, Eucalyptus camaldulensis, Aloe gilbertii, Maesa lanceolata, Erica arborea, Grevillea robusta, Lippia adoensis, Triumfetta brachyceras, and Ziziphus mauritiana (Table 1). That means 26% of the woody species of the forests were not found in this community.

3.2.3. Community 3: Combretum molle and Dodonaea angustifolia

Twenty quadrates with 61 species clustered in this community were distributed at average altitude of 1732 m a.s.l. and slope of 22. The species with high mean cover abundance in this community were Combretum molle (6.55), Dodonaea angustifolia (5.8), Rhus natalensis (5.1), Combretum collinum (4.3), and Schrebera alata (3.7).

The woody species with zero mean cover abundance in this community were Aloe gilbertii, Combretum aculeatum, Erica arborea, Eucalyptus camaldulensis, Ficus sur, Grevillea robusta, Justicia adhatoda, Lippia adoensis, Maesa lanceolata, Myrsine africana, Pappea capensis, Podocarpus falcatus, Rytigynia neglecta, Solanum incanum, Steganotaenia araliacea, Tricalysia niamniamensis, Triumfetta brachyceras, Ximenia americana, and Ziziphus mauritiana (Table 1). That means 23.8% of the woody species of the forests were not found in this community.

3.3. Community Diversity

In the forests of the study area, community 1 was the most diverse and species-rich community followed by communities 3 and 2, respectively. But the dominance () of species in the communities was decreased even though diversity of species among the communities increases. On the other hand, evenness and richness of species were increased with the decrease of dominance () among the communities (Table 2). Besides, the Univariate Analysis (UVA) on Shannon’s index (), dominance (′), evenness (), and richness showed significant variation of diversity (), difference of dominance of species (), disparity of equitable species distribution (), and variation of species richness () among the communities of the forests.

Table 2: Diversity of species in communities of the forests.

Community type
Shannon’s Index ()
Simpson’s index ()
Dominance ()
Evenness ()
Richness

1
2.951
0.892
0.108
0.904
75

2
2.855
0.882
0.118
0.897
60

3
2.905
0.888
0.112
0.903
61

3.4. Similarities of Communities in the Forests

Sörensen’s similarity coefficient computed for the floristics of the communities indicated the difference of floristics in communities 1 and 2, 1 and 3, and 2 and 3. Besides, Sörensen’s similarity coefficient computed for the floristics of the communities indicated the existence of least similarity of floristics in communities 1 and 3, as well as 2 and 3 (Table 3).

Table 3: Sörensen’s similarity of communities of study areas.

Community
Sörensen’s similarity
value

C1 and C2
0.45
0.0001

C1 and C3
0.47

C2 and C3
0.48

The Univariate Analysis (UVA) on Sörensen’s similarity coefficient computed among the communities confirmed the presence of significant difference of similarities () of communities of the forests. Hence, UVA on number of species in each community indicated the presence of significant difference in floristics () among communities of the forest.

The General Linear Model (GLM) analysis confirmed the presence of significant difference () of species distribution, altitude, and slope among the quadrates of the three community types. However, except aspect in community 3 () slope, aspect, land cover, and altitude insignificantly affected the distribution of species in communities 1, 2, and 3.

4. Discussion

Among 43 families identified, Fabaceae was the most dominant family of the forests which is similarly reported by Kuma and Shibru [15] from Oda forest. In the forests, 35% of the families had only one species for each. These families, with only one species, are susceptible to extinction either due to anthropogenic activities or due to unsuitable environmental conditions or due to both. Therefore, sound conservation and management must be given for species susceptible to extinction in in situ conditions.

In the forests, three main community types were identified. The community with large number of quadrats clustered together had highest number of species compared to that of less number of quadrats clustered together. In other words, the species richness or diversity of species was high in the community with large number of quadrats clustered together compared to the community with less number of quadrats clustered together. That means evenness and richness were increased with the increase of number of quadrats clustered in the communities of the forests. Therefore special consideration on conservation as well as management of the forests must be given for community with less number of species and for the community with less dominance () and high Shannon’s index () value.

The General Linear Model (GLM) confirmed the presence of significant difference ( value = 0.001) of species distribution, altitude, and slope among the quadrates of the three community types. However, except aspect in community 3 ( value = 0.005) slope, aspect, land cover, and altitude insignificantly affected the distribution of species in communities 1, 2, and 3. But study on separate forest (Oda only) by Kuma and Shibru [15] confirmed the presence of significant effect of altitude and slope on species distribution in the forest. This confirmed that studies on separate forest had clear indication for the environmental and climatic factors that affect the distribution of species in the communities as well as in the forest compared to that of the merged one.

Even though the forests were under protection, in support with Gurmu [16] and Ramírez-Marcial et al. [9] studies, there were major anthropogenic activities carried out in the study sites. Some of the activities seriously observed in the areas were cattle overgrazing, cutting of trees for fire wood, charcoal production and house construction, harvesting of grasses for roof cover, and setting of fire near the forest by owners adjacent to the forests to expand their land and protect crops from monkey.

In the forests mowing of grasses decrease the seeds return into seed bank by taking away from the forest; firing the forests reduces dormancy period of the seeds by damaging seed coats; and cutting of trees and grazing reduce production of seeds by reducing twigs and flower development. In support with Sumina [7], Hubbell et al. [6], Luoga et al. [8], Kennard et al. [20], and Sapkota et al. [21] the disturbances from anthropogenic activities influence the vegetation dynamics, agitate tree density at the local and regional scales, determine the size class distribution of species, important in structuring plant communities, influence species diversity in the forest community, and alter environmental conditions.

As it has been realized from the neutral informants, rising of the above factors was due to lack of knowledge and awareness and misunderstanding and dislike of enclosure of forests for conservation and management in the carbon project. Misunderstanding of the people at the vicinity was due to the consideration that the forests decline their economy by producing more destructive wild animals like hyena, leopard, and monkey.

However, the forests are sprouting different medicinal plants like Maytenus senegalensis which is used for alleviating snake bites and Maerua oblongifolia used for killing stomach worms. Besides, the forests are reducing soil erosion, generating income, increasing agricultural productivity, and stabilizing climate change in harmony with the idea of Bruijnzeel [22], Enters [23], and Wilkie and Trexler [24].

5. Conclusion and Recommendations

5.1. Conclusion

Three communities were identified in the forests of Gamuwa and Oda. Among the families, only 16 families (37.2%) had more than one species but 60.5% of the families (26) of the forests had only one species each. The families with one species only are susceptible to extinction either due to anthropogenic activities or due to unsuitable environmental conditions or due to both and need special management and in situ conservation.

In the forests 5% from community 1, 26% from community 2, 23.8% from community 3 of the species had zero mean cover abundance. That means the proportion of an area in a quadrat covered by every species was best in community 1, better in community 3, and good in community 2. In other words, the number of zero cover abundance instances indicates species richness of the community and it is inversely proportional to species richness of the community. Therefore communities with high percent of zero cover abundance should be given priority in conservation and management of the forest.

The distribution of species among the communities of the forests is insignificantly affected by average altitude and slope ( value = 0.199). But separate study carried out on Oda forest confirmed the significant effect of altitude and slope on the woody plant species distribution in the forest. This indicated that environmental factors study with respect to species distribution among the communities should be done in each forest to have clear image of influence of each environmental factors.

5.2. Recommendations

(i)As it has been newly established project on almost totally cleared off area with an aim of decreasing carbon emission, the concerned bodies should make great effort to dig out the problems and find out solutions on the burning issues of the environment.(ii)Detailed socioeconomic importance and ecological studies are required for conservation and management of the forests.(iii)Sustainable management and conservation efforts should be made through collaboration of the government, NGO, and local community to reduce carbon emission, to stabilize weather conditions, and to have effective ecosystem services.

Competing Interests

Markos Kuma declares that there is no conflict of interests regarding the publication of this article.

Acknowledgments

The author is grateful to Wolaita Sodo University for providing the fund for the activities that have been carried out in this research.

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