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Jozani biodiversity inventory report 2002 - Coastal Forests of Kenya ...

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VEGETATION CATEGORIES AND<br />

MAIN EDAPHIC FEATURES<br />

2. Albizia dominated forest, greater<br />

part covered by coral rock (Legume<br />

dominated forest <strong>of</strong> Burgess and<br />

Clarke 2000)<br />

3. Evergreen mixed dry forest or<br />

Mixed evergreen scrub forest <strong>of</strong><br />

Burgess and Clarke, 2000 (Plates<br />

23, 24).<br />

4. Dry bushland and thicket (Gillmann<br />

1949, White, 1983)(Plates 4, 5).<br />

SPECIFICATIONS AND DEFINITIONS<br />

Closed canopy formation dominated by Albizia adhianthifolia with<br />

trees 30 - 35m high. Intermediate species include Blighia unijugata,and<br />

Senna species. The Caesalpinioideae dominated dry forest suggests<br />

relicts <strong>of</strong> the former Pan-african lowland forest shown to be stable with<br />

healthy understorey regeneration (Burgess and Clarke, 2000). Mallotus<br />

opposifolia is the most dominant middle canopy tree with density <strong>of</strong><br />

about 47.5 stems.ha -1 . The habitat is the most vulnerable to fires,<br />

farming, hunting and grazing. The surface is moist, but leaf litter is<br />

thin. There are indications <strong>of</strong> former plot farms within the forest<br />

marked by ruins <strong>of</strong> long walls made <strong>of</strong> coral rocks. These were meant<br />

to prevent vermin (wild pigs) from entering the farms. It is considered a<br />

separate vegetation unit because the stands completely exclude other<br />

canopy dominant species in the next category. Many members <strong>of</strong><br />

Caesalpinioideae produce seeds <strong>of</strong> short viability which do not tolerate<br />

dessication and are not dispersed by wind or birds (Burgess and Clarke,<br />

2000). Clearance <strong>of</strong> such a forest affects regeneration potential.<br />

Relatively moist surface (surface limestone developed on coral rock),<br />

represented by a mixed dominance <strong>of</strong> a few species which include<br />

Diospyros consolatae (most dominant), Terminalia boivinii, Rapanea<br />

melanophloeus, Olea woodiana, Apodytes dimidiata, Mystroxylon<br />

aethiopicum, Maytenus mossambicensis, Ozoroa obovata and<br />

Sideroxylon inerme. In shallow valley bottoms Ficus sur is common.<br />

Canopy height is 10-25m with few emergent trees. The structure is<br />

intermediate between the bushland and thicket category (below) with<br />

trees below 10m tall and forest canopy over 25m. White (1983)<br />

recognizes that scrub forest occurs as a narrow band separating<br />

Zanzibar-Inhambane forest from the Somali-Masai regional centre <strong>of</strong><br />

endemism. Lianas are scarce or rare.<br />

This category is transitional to scrub forest and represents a dwarf<br />

bushland with clustered bushes on more xeric coral rock basement. The<br />

dominant species are the same as above, but the structure is different. It<br />

is dominated by shrubs with emergent trees to 10m. Thickets are well<br />

developed in shallow valley depressions with a thin layer <strong>of</strong> litter.<br />

Afzelia quanzensis occurs in this type <strong>of</strong> thickets. There are some<br />

indications <strong>of</strong> previous farming, thus representing secondary<br />

vegetation. Common emergent trees include Maytenus mossambicensis,<br />

Mystroxylon aethiopicum, Apodytes dimidiata, and Diospyros<br />

consolatae. All <strong>of</strong> these species occur in the previous category except<br />

that the trees are <strong>of</strong> smaller sizes (

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