|
Table 8.1. |
Kim-1
1520
m |
Kim-2 1710 m |
Kim-3
1940 m |
Kim-4
2145 m |
Kim-5
2520 m |
Lan-1 1710 m |
Lan-2 1920 m |
Lan-3 2110
m |
|
Agaurea salicifolia (Lam.) Hook. |
|
|
|
* |
|
|
|
|
|
Allanblackia ulugurensis Engl. |
* |
* |
* |
* |
|
* |
|
|
|
Alsodeiopsis schumannii (Engl.) Engl. |
* |
|
|
|
|
|
|
|
|
Aphloia theiformis (Vahl) Benn. |
|
|
* |
* |
|
* |
* |
* |
|
Berberis holstii Engl. |
|
|
|
|
* |
|
|
|
|
Canthium oligocarpum Hiern subsp. |
|
|
|
|
|
* |
* |
|
|
Cassipourea gummiflua Tul. |
|
|
|
|
* |
|
|
* |
|
C. malosana (Baker) Alston |
* |
* |
* |
* |
|
* |
* |
* |
|
Chrysophyllum gorungosanum Engl. |
* |
|
|
|
|
|
|
|
|
Cornus volkensii Harms |
|
* |
|
|
|
|
|
|
|
Cryptocarya liebertiana Engl. |
|
|
|
|
|
|
* |
|
|
Dichapetalum eikii Ruhl. |
* |
|
|
|
|
|
|
|
|
Dracaena afromontana Mildbr. |
|
* |
* |
|
|
|
|
|
|
Faurea wentzeliana Engl. |
|
|
|
* |
|
|
|
|
|
Ficalhoa laurifolia Hiern |
* |
|
|
|
|
|
* |
* |
|
Garcinia volkensii Engl. |
* |
* |
* |
* |
|
* |
* |
* |
|
Ilex mitis (L.) Radlk. var. mitis |
* |
* |
* |
* |
|
* |
* |
* |
|
I. mitis (L.) Radlk. var. schliebenii Loes. |
|
|
|
|
* |
|
|
|
|
Lasianthus cereiflorus E.A. Bruce |
* |
* |
* |
* |
|
|
|
|
|
Lepidotrichilia volkensii (Gurke) J.-F. |
|
|
|
* |
|
|
|
|
|
Lijndenia brenanii (A. & R. Fernandes) |
* |
|
|
|
|
|
|
|
|
Macaranga kilimandscharica Pax |
|
|
|
|
|
* |
|
* |
|
Maesa lanceolata Forssk. |
* |
* |
* |
|
|
|
|
|
|
Maytenus undata (Thunb.) Blakelock |
|
* |
* |
|
|
|
|
|
|
Memecylon myrtilloides Markgr. |
|
|
|
|
|
|
* |
|
|
Mosteua brunonis Didr. |
|
|
|
|
|
* |
* |
|
|
Myrianthus holstii Engl. |
|
* |
|
|
|
|
|
|
|
Ochna holstii Engl. |
|
|
|
* |
|
|
* |
|
|
Ocotea usambarensis Engl. |
|
|
|
* |
|
* |
* |
* |
|
Oxyanthus speciosus DC. |
|
|
|
|
|
* |
* |
|
|
Parinari excelsa Sabine |
* |
|
|
|
|
|
|
|
|
Pauridiantha paucinervis (Hiern) |
* |
* |
|
|
|
|
|
|
|
P.
symplocoides (Moore) Bremek. |
|
|
* |
|
|
|
|
|
|
Peddiea
puberula Domke |
|
|
|
* |
* |
|
|
|
|
Piper
capense L.f. |
|
* |
* |
|
|
|
|
|
|
Pittosporum
goetzei
Engl. |
|
|
|
|
* |
|
|
|
|
Podocarpus henkelii Stapf |
|
|
|
* |
* |
* |
* |
* |
|
Rapanea
melanophloeos (L.) Mez |
* |
* |
|
* |
* |
* |
* |
* |
|
Rawsonia
reticulata Gilg |
|
|
* |
|
|
|
* |
|
|
Rhipidantha
chlorantha
(K. Schum.) |
|
* |
|
|
|
|
|
|
|
Rytigynia
lichenoxenos
(K. Schum.) |
* |
|
|
|
|
* |
|
|
|
Schefflera
lukwangulensis (Engl.) Engl. |
* |
|
* |
* |
|
|
* |
* |
|
Symphonia
globulifera L.f. |
* |
* |
* |
* |
|
* |
* |
|
|
Syzygium
guineense (Willd.) DC. subsp. |
* |
|
* |
* |
|
|
|
|
|
Syzygium
parvulum Mildbr. |
|
|
|
|
* |
|
* |
|
|
S.
sclerophylum
Brenan |
|
|
|
|
* |
* |
|
|
|
Zenkerella
capparidacea (Taub.) J. Leon. |
* |
* |
|
|
|
|
|
|
Table 8.1. Eastern Arc endemics are marked with an asterisk in
front of the name, Uluguru endemics with two asterisks in front of the name.
The plots at Kinhandu-1 (1520 m) and lanzi-1 (1710 m) were not very far from
the forest edge and were affected by human disturbance.
|
Table 8.2. |
Total BA (m2/ha) |
No. of stems |
No. of individuals |
No. of species |
Canopy base |
Height of midstorey |
Height of canopy |
Height of emergents |
|
Kim-1 1520 m |
141.57 |
91 |
84 |
26 |
5-6 m |
10-12 m |
20-30 m |
40 m |
|
Kim-2 1710 m |
39.64 |
152 |
145 |
34 |
3-4 m |
6-8 m |
20-30 m |
55 m |
|
Kim-3 1940 m |
50.21 |
157 |
142 |
28 |
6-10 m |
10-15 m |
25-30 m |
45 m |
|
Kim-4 2145 m |
136.12 |
146 |
141 |
27 |
6-8 m |
10-12 m |
20-25 m |
35 m |
|
Kim-5 2520 m |
37.28 |
170 |
136 |
17 |
3-5 m |
5-7 m |
12-15 m |
25 m |
|
Lan-1 1710 m |
99.81 |
101 |
98 |
20 |
6-8 m |
15-20 m |
24-28 m |
40 m |
|
Lan-2 1920 m |
89.20 |
233 |
222 |
30 |
6-8 m |
15-20 m |
25-30 m |
40 m |
|
Lan-3 2110 m |
82.75 |
100 |
93 |
18 |
8-10 m |
20-25 m |
27-30 m |
40 m |
Table
8.2. Unidentified species are
included. At the Kimhandu-5 (2520 m) plot there were dense stands of bamboo.
These are not included which should be taken into consideration for
interpretation of number of stems and basal area.
|
Table 8.3. |
Kim-1 1520 m |
Kim-2 1710 m |
Lan-1 1710 m |
Lan-2 1920 m |
Kim-3 1940 m |
Lan-3 2110 m |
Kim-4 2145 m |
Kim-5 2520 m |
|
Simpson index |
4.06 |
4.82 |
2.19 |
11.97 |
5.86 |
3.73 |
4.05 |
4.16 |
|
Equitability |
0.15 |
0.14 |
0.11 |
0.40 |
0.21 |
0.21 |
0.15 |
0.24 |
|
Shannon index |
1.68 |
2.19 |
1.20 |
2.69 |
2.12 |
1.70 |
1.82 |
1.71 |
|
Equitability |
0.51 |
0.62 |
0.40 |
0.79 |
0.64 |
0.59 |
0.55 |
0.60 |
|
No. of species |
26 |
34 |
20 |
30 |
28 |
18 |
27 |
17 |
Table 8.3.
Three different diversity measures are used to
asses the diversity in the plots:
The
Simpson index: D = åni (ni - 1) ]/[N(N - 1)] , where ni = the basal area of the ith species,
and N = the total basal area. The reciprocal of the Simpson index is used so
that the value of the index increases with increasing diversity. Simpson's
index is biased towards showing species evenness, equitability is expressed as
the index proportion of total number of specieas. The Shannon index: H'= åpi ln pi , where pi is the proportional basal area (ni/N) of the ith
species. Shannon's index which is biased towards species richness (Magurran
1988) equitability is expressed as the index proportion of ln to total number
of species. The total number of species. This is a simple expression of the
numbers of species recorded in each plot.