SINET: Ethiop. J. Sci., 40(2):60-73, 2017 ISSN: 0379–2897 (PRINT)
© College of Natural Sciences, Addis Ababa University, 2017 ISSN: 0379–2897
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Author to whom correspondence should be addressed.
DIVERSITY, ABUNDANCE AND THREATS OF AVIAN SPECIES IN KOGA DAM AND
ITS SURROUNDINGS, NORTH-WESTERN ETHIOPIA
Dessalegn Taye
1
and Melaku Wale
2,*
1
Biodiveristy Institute, Bahir Dar, Ethiopia. E-mail: tayedessalegn@gmail.com
2
Bahir Dar University, P O Box 79, Ethiopia. E-mail: melakuwale@gmail.com
ABSTRACT: A survey of birds was conducted in Koga Dam Reservoir of the Amhara Region, Northwestern
Ethiopia from October 2010 to March 2011. The objective of the study was to assess the diversity of birds and
anthropogenic activities in the Dam and its environs. Data collection methods included transect method, interviews,
and direct observations. Three habitats were identified for the study, i.e., wetland, farmland and scrubland. Diversity
indices including Shannon diversity index were used for data analysis. The results showed that a total of 103 bird
species belonging to 75 genera, 24 families and 11 orders were found. Charadriiformes appeared to be the most
dominant order represented by 8 families and 25 species, followed by Passeriformes with 5 families and 15 species.
The least was Phoenicopteriformes, Coraciiformes and Strigiformes, with1 family and 3 species each. Bird diversity
was high in the scrubland (H′=3.96) and low in the farmland (H′=3.20) during the wet season. The highest species
richness during both seasons was recorded in wetland (65) followed by farmland(55). The least species number was
recorded in the scrubland (53). The newly constructed dam has changed the species composition and feeding habits
of birds. After the construction of the dam, new bird species arrived and the number of natives increased. According
to farmers, after the construction of the dam, seed feeder birds, unlike carnivores, shifted their feeding habits from
the wetland to crops and became pests. Anthropogenic threats such as clearing of natural vegetation, sedimention,
over-grazing, recesssion farming and over exploitation of other resources all contribute to the decline of the bird
species. Thus, appropriate measures must be taken to re-stabilize the bird habitat.
Key words/phrases: Bird species, Change of habitat, Diversity, Reservoir.
INTRODUCTION
Ethiopia is a country of great geographic diversity
with wide altitudinal and physiographic variation.
The altitude ranges from 116 meters below sea
level in the Danakil Depression to the highest peak
of 4,653 meters above sea level on Mount Ras
Dashen. Ethiopia is rich in biodiversity and 7
thousand km
2
of its 1.1 million km
2
area is covered
by water (Yilma Delelegn and Geheb, 2003).
Ecosystems range from dry lowlands to humid
forests, wetlands to cool highland plateaus
resulting in variable climate, topography and
vegetation and unique biota with high level of
endemism (EWNHS, 1996). Ethiopia has established
about 73 Important Bird Areas (IBAs), 30 of which
comprise wetlands, while the rest represent other
ecosystems (Shimelis Aynalem and Afework
Bekele, 2008).
Birds are considered as useful biological
indicators because they ecologically adapt to all
kinds of habitats (Sivaperuman and Jayson, 2006).
Wetlands are important habitats of fauna
(Ramseur Convention Bureau, 2000; Beury et al.,
2008). However, the importance of wetlands
depends on different factors (wetland size,
diversity of vegetation, water quality, food
resources and topography) (Mitsch and Gosselink,
2000). In wetlands, birds breed, nest and teach
young, drink water, feed, rest, shelter and interact
(Bibby et al., 1998). Wetlands provide food for
birds such as plants, vertebrates, and invertebrates
(Ramseur Convention Bureau, 2000).
Birds are the most conspicuous, with
specialized traits evolved to exploit the resources
of habitats in rivers and wetlands (Ormerod and
Tyler, 1993; Buckton and Ormerod, 2002). The
effect of environmental change on the distribution,
abundance and range of river birds is often
reduced (Ormerod et al., 1986; Ormerod and Tyler
1993; Colombari and Cordiner, 1999; Ormerod et
al., 2000).