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Family / Scientific name - Coastal Forests of Kenya and Tanzania

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REMP Technical Report 44: Biodiversity Summary<br />

2. Observations<br />

Observations are made with the aid <strong>of</strong> a Petzel head torch with a halogen bulb. This torch picks<br />

out eye shine that is reflected by nocturnal mammals. Once eye shine is spotted, a four cell<br />

Maglite torch is used with binoculars (Zeiss DDR 10x50W), to obtain observations <strong>of</strong> the<br />

animal(s). Notes are made <strong>of</strong> the height <strong>of</strong> the animals in the canopy, support use, general<br />

behaviour <strong>and</strong> animal interactions.<br />

3. Trap data<br />

Chardonneret traps baited with fruit are used to capture galagos alive <strong>and</strong> sometimes bat nets are<br />

used to catch trap shy species. Traps are checked every 4-6 hours, <strong>and</strong> animals are extracted by<br />

h<strong>and</strong> without the need for anaesthesia. Biometric measurements are taken <strong>and</strong> tissue samples<br />

(from the ear, using a biopsy punch) are collected for genetic analysis <strong>and</strong> stored in ethanol.<br />

4. Population <strong>and</strong> ecological data<br />

Night walks are conducted along pre-existing paths where possible to reduce noise <strong>and</strong><br />

disturbance. Galago sightings <strong>and</strong>/or calls are noted. From this, relative densities are estimated<br />

by counting the number <strong>of</strong> galagos encountered over a measured distance. Given a known<br />

distance from the path within which animals can be counted reliably <strong>and</strong> the distance sampled, it<br />

is possible to estimate the number animals within that particular area. This estimate is usually<br />

very approximate <strong>and</strong> is biased by such factors as; detection ability, variability in habitat <strong>and</strong><br />

moon phase. Only by intensively trapping <strong>and</strong> marking (preferably radio tracking) <strong>of</strong> animals<br />

from a given known area can density estimates be properly made (Harcourt <strong>and</strong> Nash, 1986;<br />

Bearder <strong>and</strong> Martin, 1979). Encounter rates per hour can also give an indication <strong>of</strong> relative<br />

animals densities as well as activity rates under variable weather conditions <strong>and</strong> moon phases.<br />

5. Any other data.<br />

Other data collected opportunistically include; galago hairs, faeces <strong>and</strong> locating tree holes or nests<br />

where the animals may live during the daytime.<br />

Results<br />

Galagos<br />

Five species <strong>of</strong> galago were recorded from the study sites visited (see Table 1). A sixth species,<br />

suspected to be the Senegal galago was recorded in the Selous game reserve near S<strong>and</strong> Rivers<br />

Safari camp. This observation requires confirmation.<br />

Table 1. Galago records for the field sites visited south <strong>of</strong> the Rufiji River.<br />

Species/Site Kichi Hills FR Nyamuete FR Kiwengoma FR<br />

Garnett’s Galago<br />

Present in Present in forest Present in forest<br />

Otolemur garnetti<br />

forest<br />

Large Eared greater galago Not recorded Not recorded Present in Miombo<br />

Otolemur crassicaudatus<br />

woodl<strong>and</strong>/ forest edge<br />

Senegal galago<br />

Not recorded Not recorded Not recorded<br />

Galago senegalensis<br />

Mohol galago<br />

Galago moholi<br />

Grant’s Galago<br />

Galagoides granti<br />

Zanzibar Galago<br />

Galagoides zanzibaricus<br />

Present<br />

miombo<br />

woodl<strong>and</strong><br />

in Not recorded Not recorded<br />

Present<br />

forest<br />

in Present in forest Present in forest<br />

Not recorded Not recorded Not recorded<br />

93

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