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Environmental and Social Impact Assessment - Gibe III

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<strong>Gibe</strong> <strong>III</strong> – <strong>Environmental</strong> <strong>and</strong> <strong>Social</strong> <strong>Impact</strong> <strong>Assessment</strong> 300 ENV R CS 002 C - A9003099<br />

5.2.3 Aquatic Ecology<br />

The consultant has carried out an aquatic ecology assessment <strong>and</strong> the activities include the following:<br />

• Inventoried the composition of the riverine <strong>and</strong> riparian fauna (invertebrates, plankton, benthos, etc)<br />

of the Omo river at three critical points along the future reservoir area - Omo bridge, dam site <strong>and</strong><br />

confluence of Gojeb-<strong>Gibe</strong> rivers;<br />

• Made a comprehensive habitat integrity assessment of the Omo river at two sites;<br />

• Assessed the potential impact of the creation of a reservoir on the riparian <strong>and</strong> riverine fauna, disease<br />

vectors, rare biota, etc.<br />

Available literature was reviewed for previous studies done on aquatic communities of invertebrates in the<br />

Omo basin. The major references consulted were studies conducted at the Gojeb, <strong>Gibe</strong> <strong>and</strong> Omo rivers by<br />

Golubstov <strong>and</strong> Mina (2003) which summarizes the scientific results of the Joint Ethiopian-Russian<br />

Biological Expedition (JERBE) <strong>and</strong> ESIA reports of Gilgel <strong>Gibe</strong> I, <strong>and</strong> Gojeb Hydropower Projects.<br />

Rapid habitat integrity assessment was made at the Omo bridge <strong>and</strong> confluence sites using the criteria<br />

developed for South African rivers by Kleynhams (1996) <strong>and</strong> the Rapid Bioassessment Protocol (RBP) of<br />

EPA (1999). A few criteria were modified to suit the local conditions, such as pollution by dung <strong>and</strong> human<br />

wastes. Weights are assigned to different in-stream <strong>and</strong> riparian characters of the river reach such as flow<br />

modification, exotic macrophytes, bank erosion <strong>and</strong> vegetation cover. The ten most important habitat<br />

components are considered for analysis with each component having a score of 10 points, adding up to a<br />

total of 100 percent. A range of score points describe the habitat integrity status of the river. High scores<br />

describe unimpaired conditions <strong>and</strong> low percentages apply to impacted rivers.<br />

5.2.3.1 Riparian fauna - Omo bridge site<br />

Table 5.32 lists some of the dominant riparian macro-invertebrates identified at the Omo Bridge.<br />

Grasshoppers <strong>and</strong> crickets (Order Orthoptera) made up the most abundant group, in terms of biomass, <strong>and</strong><br />

butterflies in terms of diversity. Butterfly species such as Colotis <strong>and</strong> Odonata such as dragonflies were<br />

noted on the bank. Observations of the riparian fauna indicate the predominance of grasshoppers (Acrididae<br />

<strong>and</strong> Oxydae), damselflies, beetles <strong>and</strong> Hemipteran bugs.<br />

Table 5.32: Riparian macro-invertebrates at the Omo bridge<br />

Common name Scientific names Relative abundance<br />

Meadow grasshoppers<br />

Field crickets<br />

Butterflies<br />

Preying mantis<br />

Forest damselflies<br />

Blue damselfly<br />

Beetles<br />

Unidentified bugs<br />

Acrida sp.<br />

Oxya sp.<br />

Gryllus sp.<br />

Colotis sp.<br />

Pieris sp.<br />

Delais sp.<br />

Belenois sp.<br />

Pareronia sp.<br />

Order Dictoptera<br />

Fam. Platycnemidae<br />

Enallagma sp.<br />

Several species<br />

Several species<br />

Note: + indicates common, ++ very common <strong>and</strong> +++ highly abundant<br />

CESI SpA - Mid-Day International Consulting Engineers Page 130<br />

+++<br />

+++<br />

+++<br />

+++<br />

+<br />

+<br />

+<br />

+<br />

+<br />

+<br />

+<br />

++<br />

+

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