www.tropicalplantresearch.com 292 Received: 11 March 2016 Published online: 30 June 2016

ISSN (E): 2349 1183

ISSN (P): 2349 9265

3(2): 292319, 2016

Research article

Plant diversity and community analysis of the vegetation around

Tulu Korma project centre, Ethiopia

Zewdie Kassa1,2*

, Zemede Asfaw1 and Sebsebe Demissew

1

1Department of Plant Biology and Biodiversity Management, the National Herbarium, Addis Ababa University,

P.O. Box: 3434, Addis Ababa, Ethiopia 2Department of Biology, Mizan-Tepi University, P.O. Box, 260, Tepi, Ethiopia

*Corresponding Author: zewdiekasa@gmail.com [Accepted: 23 June 2016]

Abstract: A study on plant diversity and community analysis was conducted between October

2014 to September 2015 with the objective of documenting plant species diversity together with

the status and trends of biodiversity change. Common ecological methodologies and techniques

were applied. Aerial photographs using Google earth and ground survey using GPS, compass and

clinometers supported by ArcGIS based mapping was done to identify the clear distinction

between vegetation and habitat heterogeneity before vegetation sampling. R statistical Software

was used to run cluster analysis and ordination. Four plant community types were identified in the

study. The Shannon-Weiner Diversity index was calculated to see the overall diversity of the study

area. The area is with relatively high plant species diverse at H= 3.37 with overall species

evenness, J= 0.61 confirming the fact that Shewa floristic region is among the most species rich

habitats. Ordination results showed that the major environmental variables structuring the floristic

composition and plant community types and altitude was found to be the most influential factor at

95% confidence interval (P=0.005) using Canonical Correspondence Analysis. Comparison of

historical records from literature and practical observation of the current status of the study area

confirmed that there is an increasing trend of biodiversity and vegetation cover. This is justified by

observing the positive impacts of the project centre for indigenous trees propagation and

biodiversity development for Ethiopia located at Tulu Korma. The study showed that the area is

rich in plant species and floristic composition, hence, experiences adopted by the Project Centre

should be the lessons learned for the restoration and rehabilitation of similar environments.

Keywords: Cluster analysis - Ordination - Multipurpose plants - Indigenous species - Restoration.

[Cite as: Kassa Z, Asfaw Z & Demissew S (2016) Plant diversity and community analysis of the vegetation

around Tulu Korma project centre, Ethiopia. Tropical Plant Research 3(2): 292319]

INTRODUCTION

Biodiversity is the variability among living organisms from all sources including inter alia, terrestrial,

marine and other aquatic ecosystems and the ecological complexes of which they are part; this includes diversity

within species, between species, and of ecosystems. In a broad sense it is to mean the abundance and

distributions of and interactions between genotypes, species, communities, ecosystems and biomes. The term

inter alia above is to mean among other things (Reynolds 2000, Gaston et al. 2004, Leadley et al. 2010, CBD

2011).

For countries like Ethiopia, it is important to learn the success histories from other countries as well as

certain ongoing project trials in some parts of the country to rehabilitate degraded habitats, ecosystems and

biodiversity loss. Ecological restoration is an attempt to return a system to some historical state, although the

difficulty or impossibility of achieving the aim is widely recognized (Guyton 2001, Palmer et al. 2006, Naeem

et al. 2009, Ferwerda 2012). A more realistic goal may be to move a damaged system to an ecological state that

is within some acceptable limits relative to a less disturbed system. Ethnoecological approaches are among the

key options in integrating academic disciplines and traditional ecological knowledge for sustainable

environment (Albuquerque et al. 2014, Berkes et al. 1995, Berkes et al. 2000, Gmez-Baggethun et al. 2013).

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This research project focused on studying the status and trends of biodiversity change in Tulu Korma and its

surrounding areas of Ejere District. Tulu Korma and its surrounding where the study was carried out is the

Center for Indigenous Trees Propagation and Biodiversity Development in Ethiopia. The formerly known as

Center for Indigenous Trees Propagation and Biodiversity Development in Ethiopia and currently named as

Center for the Restoration of Ethiopias Biodiversity and Key Natural Resources was founded by Professor

Legesse Negash and established on 10 July 2004 with its primary objectives which envisages providing a

platform for research and development on indigenous trees, shrubs, biodiversity, watersheds, and key natural

resources including water and soils (Legesse Negash 2010).

MATERIALS AND METHODS

Location

Tulu Korma is located at 5055 km West of Addis Ababa on the high way running from Addis Ababa to

Ambo between 0901.188 N and 03821.570 E within altitude range of 2,1632,267m. (Legesse Negash,

2010). Four neighboring kebeles bordering Tulu Korma are Chiri to the north, Kimoye to the west, Hora to the

south and Endode to the east. Addis Alem is the nearest town about 3 kilometers from the center and it is with

weather station from where the Ethiopian National Meteorological Service Agency (ENMSA) record weather

data (Zewdie Kassa et al. 2016) (Fig. 1).

Figure 1. Location of the study area.

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Climate

According to Zewdie Kassa et al. (2016), the annual average minimum and average maximum temperature

for 16 years data is 7.4C and 26.2C respectively. The annual average temperature and average rainfall for the

same years data are 16.9C and 1099 mm respectively (Fig. 2).

Figure 2. Climate diagram of the study area (data from ENMSA).

Vegetation

Areas between altitudes of 1800 and 3000 meters have been marked as the Dry evergreen Afromontane

forest and grassland complex with the exception of high annual rainfall areas of 1700 millimeters and above

(Friis et al. 2011). The vegetation of Tulu-korma and its surrounding belongs to such vegetation type and

characterized by a canopy dominated by Juniperus procera (Cupressaceae), Podocarpus falcatus

(Podocarpaceae), Olea europaea subsp.Cuspidata (Oleaceae), Croton macrostachyus (Euphorbiacea) and Ficus

spp. (Moraceae). Shrubs and bush lands, woodlands and plantations are also available.

GIS data collection

It was noted that geographical information systems and models are among Computer-based Decision

Support Tools integrating information (Mishra & Agarwal 2015). Hence, both aerial photographs using Google

earth and ground survey using GPS, compass and clinometers supported by ArcGIS based mapping was done to

identify the clear distinction between vegetation and habitat heterogeneity before vegetation sampling. Due to

habitat heterogeneity, preferential sampling technique was used to collect vegetation and floristic data.

Vegetation and Ecological Data Collection

Vegetation data were collected using preferential sampling techniques and cover abundance values were

calculated using presence/absence method (Kent & Cocker 1992). Cover was calculated as the area of the

ground within a quadrate which is occupied by the above ground parts of each species when viewed from above

(canopy cover) visually estimated as percentage. A 30m 30m square quadrate was used to sample plant

species. Sub-quadrates of 2m 2m for grasses and sedges, 5m 5m for herbs, 10m x 10m for shrubs were used

to estimate the cover abundance values of different plant habits. The layouts of the quadrates were in such a way

that one from each corner of the large quadrate and one at the center for the respective life forms. Species

abundance values were converted following the Braun-Blanquet 19 scales (Van Der Maarel 2005) by

calculating the Ordinal Transformed Values (OTV) as,

OTV = 1.415 Where, ln is the natural logarithm and C is the cover abundance value in percentage. The vegetation data were

arranged in a three column format (sites, species and abundance) of creating ecological data tables for ease of

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analysis using R statistical software following (Zerihun Woldu 2012). The data were then carefully inspected in

the three column table to check for possible errors before analysis.

Ecological data such as altitude, latitude, longitude, slope and aspect were collected by setting the GPS on

the projected coordinate system format (UTM_Adindan_Zone 37). Aspect and slope were also carefully

recorded by using SILVA compass and SILVA Ranger Clinometers instruments respectively right during

specimen collection. Geophysical features, presence/absence an