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Journal of Natural Sciences Research
ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online)
Vol.3, No.12, 2013

www.iiste.org

Vegetation Analysis of Ngel Nyaki Forest Reserve, Mambilla
Plateau, Nigeria
Aderopo Akinsoji
Department Of Botany, University Of Lagos.
Email: aderopoakinsoji@yahoo.com
Abstract
The vegetation of Ngel Nyaki Forest Reserve, Nigeria was analysed using data gathered with point-centred
quarter method. 80 trees belonging to 29 species distributed in 21 families were encountered. The density of
trees was 785 trees per hectare. The girth-size distribution curve indicated that the vegetation of Ngel Nyaki is
stable and self-sustaining. The more dominant species based on Importance Values are Poulteria altissima,
Polyscias fulva, Carapa grandiflora and Entandrophragma angolense. The least dominant species are Dombeya
ledermanii, Celtis occidentalis and Croton macrostachyus.
Keywords: Ngel Nyaki Forest Reserve, Mambilla Plateau, vegetation analysis
1. Introduction
The forests of Nigeria form part of the Guinean forest biodiversity hotspot which extends from Sierra Leone to
Cameroon mountains. The Cameroon highlands are fragmented and extends to eastern parts of Nigeria where
they form montane and sub-montane forests. One of such fragmented forests is Nge lNyaki Forest Reserve
(NNFR) which was gazetted as a forest reserve in 1969. NNFR which is located on the western escarpment of
Mambilla Plateau in the south eastern corner of Taraba State, Nigeria at an altitude of 1450-1600m asl is a
mosaic of mountain top grassland and sub-montane closed canopy forest limited to the streams’ valleys (Fig. 1).
NNFR (07o 141 N 11o 041 E) covers an area of about 46km2 with a woody plant density of 669/ha (Ihuma et al,
2011). NNFR is one of the most floristically diverse montane –submontane forest stands in Nigeria (DowsettLemaire, 1989) and the most diverse on Mambilla plateau (Chapman and Chapman, 2001). It contains many
plants which are endemic to the afromontane region of White (1983). This high level of endemism makes the
forest a priority for conservation (Fishpool, 1997). NNFR has more than 146 vascular plants out of which 25 are
in the IUCN Red Data List (Borokini et al., 2012) four of which are endangered and several are new to Nigeria
(eg. Anthonotha noldeana) (Chapman and Chapman, 2001). The forest is also rich in birdlife (Ihuma et al, 2011)
and has been classified as an Important Bird Area by Birdlife International and a critical site for biodiversity
conservation (Ezealor, 2002). The climate is seasonal with dry season lasting from November to March and
rainy season from April to October with a mean annual rainfall of 1780mm (Chapman and Chapman, 2001). The
need to compare vegetation from different locations requires objective analysis of quantitative data. Akinsoji et
al, (2003) stated that quantitative data obtained from objective sampling procedures is required for comparative
purposes.Two methods used in gathering vegetation data are Count Plot methods (quadrats) and Plotless
methods, also called Wisconsin Distance Methods (Mueller-Dombois and Ellenberg, 1974). Plotless methods are
preferred because they are less laborious and time conserving. Of the four plotless techniques the one found to be
most efficient is the point-centred quarter method (Cottam and Curtis, 1956). It has been widely used with
satisfactory report in North America ( Caplenor, 1968, Boorman and Buell, 1964; Bray and Curtis, 1957) and in
Nigeria (Akinsoji et al, 2003).
Ngel Nyaki Forest Reserve is a fertile ground for research in tropical biology and conservation because of its
diversity and level of endemism. The Nigerian Montane Forest Project has pioneered the research in NNFR and
contributed immensely to literature. This study which is a phytosociological analysis of the sub-montane forest
using point-centred quarter method is to complement the work done so far in NNFR.
2. Materials And Methods.
At each sampling station, a baseline was established parallel to the forest edge. A transect perpendicular to the
baseline was also established and a sampling point was located at a distance determined by a figure from random
table. At each sampling point, four quarters were marked with the sampling point as the origin. The nearest tree
to the origin in each quarter was identified. Its distance from the origin was recorded and its girth at breast height
was also recorded. This procedure was carried out at 20 randomly selected points in the forest reserve. The few
species that could not be identified in the field were taken to Forestry Research Institute Herbarium at Ibadan.
All the distances were added together and a mean distance (d) was calculated. The mean area was computed as
d2.. Using this value, the absolute density of trees per hectare was calculated as 10,000/d2. From this the
absolute densities of each species was calculated and then relative densities. Frequency was calculated as the
number of sampling points a species occurred divided by the total number of sampling points. Species
dominance was calculated as basal area of a species divided by the total number of all species. Basal area (A)

121
Journal of Natural Sciences Research
ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online)
Vol.3, No.12, 2013

www.iiste.org

was calculated as A= c2 / 4.pi where c circumference and pi = 3.14. Relative frequency and relative dominance
of each species was calculated. The three relative values were added together to obtain Importance Values (IV)
for the species and they were ranked according to the magnitude of their IV.

Fig. 1: Map of Southeastern Taraba State Showing Ngel Nyaki Forest Reserve.
3. Results and Discussion
The forest is a closed canopy forest with gaps in places where there had been tree falls. A total of eighty trees
belonging to twenty nine species distributed in twenty one families were recorded (Table 1). Most of the forest is
relatively undisturbed but the edges are subjected to burning by incursions of grass land fires. Although the
density of the forest trees was estimated to be 785 trees per hectare which is higher than the estimate of Ihuma et
al, (2011), the actual density may be higher because the point-centred quarter method is known to underestimate
absolute density of trees (Akinsoji et al., 2003, Skarpe, 1990) and species richness thus rarer species tend to be
missed out. The girth size distribution

122
Journal of Natural Sciences Research
ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online)
Vol.3, No.12, 2013

www.iiste.org

Table 1. Tree Species Composition Of Ngel Nyaki Forest Reserve Sampled With Point-Centred Quarter
Method.
SPECIES
Anthonotha noldeae
Beilshmeidea mannii
Carapa grandiflora
Celtis occidentalis
Chrysophyllum albidum
Croton macrostachyus
Deinbolia pinnata
Diospyros montbutensis
Dombeya ledermanni
Entandrophragma angolense
Ficus sp.
Garcinia smeathmeanii
Isolona deightonii
Khaya grandifoliola
Leptaulus zenkeri
Macaranga occidentalis
Oxyanthus speciosus
Pleiocarpa pycnantha
Polyscias fulva
Poulteria altissima
Pterygota mildbraedii
Santiria trimera
Strombosia schefflerii
Symphonia globulifera
Syzygium guineense
Tabernaemontana contorta
Treculia obovoidea
Trichilia prieuriana
Zanthxylum zanthxyloides

FAMILY
Leguminosae-Caesalpinoideae
Lauraceae
Meliaceae
Ulmaceae
Sapotaceae
Euphorbiaceae
Sapindaceae
Ebenaceae
Sterculiaceae
Meliaceae
Moraceae
Clusiaceae
Annonaceae
Meliaceae
Icacinaceae
Euphorbiaceae
Rubiaceae
Apocynaceae
Araliaceae
Sapotaceae
Sterculiaceae
Burseraceae
Olacaceae
Clusiaceae
Myrtaceae
Apocynaceae
Moraceae
Meliaceae
Rutaceae

of trees (Fig. 2) shows that more of the trees fall within the smaller girth size classes and typifies the Type 1
curve of Obot (1991) which represents a stable self –sustaining plant population. There is more of smaller trees
to replace the more mature trees when they reach senescence. The phytosociological analyses of NNFR are
summarized in Table 2. Because of the underestimation of tree density and species richness due to the methods,
relative values are employed to determine Importance values of species as an indicator of their dominance status
in the community. The more dominant species in order of IV rankings are Poulteria altissima, Polyscias fulva,
Carapa grandiflora and Entandrophragma angolense. Although P. altissima has low density and frequency
values, but its large dominance value accounts for its overall dominance. The least dominant species are
Dombeya ledermanni, Celtis occidentalis. and Croton macrostachyus. Their density, frequency and dominance
values were comparatively small.

123
Journal of Natural Sciences Research
ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online)
Vol.3, No.12, 2013

www.iiste.org

35

Number of trees

30
25
20
15

No of trees
10
5
0
0-20

21-40

41-60

61-80

81-100

>-9

Girth Size Class (cm)
Fig. 2: Girth Size Distribution of Trees In Ngel Nyaki Forest Reserve.
Table 2. Phytosociological Analyses Of Data Collected From Ngel Nyaki Forest Reserve
SPECIES
Poulteria altissima
Polyscias fulva
Carapa grandiflora
Entandrophragma angolense
Garcinia smeathmeanii
Trichilia prieuriana
Ficus sp.
Anthonotha noldea
Syzygium guineense
Pleiocarpa pycnantha
Macaranga occidentalis
Strombisia scheffleri
Oxyanthus speciosus
Deinbollia pinnata
Tabernaemontana contorta
Leptaulus zenkeri
Chrysophyllum albidum
Khaya grandifoliola
Diospyros montbutensis
Beilshmiedia manni
Isolona deightonii
Zanthoxylum zanthoxyloides
Treculia obovoides
Pterygota mildbraedii
Santiria trimera
Symphonia globulifera
Dombeya ledermanii
Celtis occidentalis
Croton macrostachyus

*RDe
2.5
6.2
6.2
3.8
7.5
7.5
5
3.8
3.8
5
5
5
3.8
3.8
3.8
3.8
2.5
2.5
2.5
2.5
2.5
2.5
1.2
1.2
1.2
1.2
1.2
1.2
1.2
124

*RF
2.9
7.1
5.7
2.9
7.1
7.1
4.3
4.3
4.3
5.7
4.3
2.9
4.3
4.3
2.9
2.9
2.9
2.9
2.9
2.9
1.4
1.4
2.4
1.4
1.4
1.4
1.4
1.4
1.4

*RDo
17.3
6.8
7.1
11.6
3.6
3.6
4.9
5.9
4.9
2
2.1
3.1
2.7
1.5
2.1
1.9
2.2
2.2
1.3
1.3
1.2
0.9
1.9
1.8
1.7
1
0.89
0.89
0.5

*IV
22.7
20.1
19
18.3
18.2
18.2
14.2
14
13
12.7
11.4
11
10.8
9.6
8.8
8.6
7.6
7.6
6.7
6.7
5.1
4.8
4.5
4.4
4.3
3.6
3.5
3.5
3.1
Journal of Natural Sciences Research
ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online)
Vol.3, No.12, 2013

•
•
•
•

www.iiste.org

RDe- Relative Density
RF - Relative Frequency
RDo-Relative Dominance
IV - Importance Value

4. Acknowledgement
I thank the Nigerian Montane Forest Project for permission to work in Ngel Nyaki Forest Reserve, Sikiru Kadiri
and Saidu Mayosabere for field assistance and the entire Yelwa community. Dr. Tope Adeyemi prepared the
figures. This study was funded by University of Lagos Central Research grant M2010/07.
References.
Akinsoji, A., Ayanbamiji, T, and Durugbo, E. U. 2003. Comparative phytosociological analysis in the GashakaGumti National Park using point-centred quarter and quadrat methods. Nigerian Journal of Botany 16:133-143.
Borokini, T.I., Babalola, F. D., Amusa, T. O., Ivande, S. T., Wala, Z. J., Jegede, O. O., Tanko, D. and Ihuma, J.
O. 2012. Community-based forest resources management in Nigeria: Case study of Ngel Nyaki Forest Reserve,
Mambilla Plateau, Taraba State, Nigeria. Journal of Tropical Forestry and Environment 2(1):69-76.
Boorman, F. H. and Buell, M.F. 1964. Old-age stand of hemlock-northern hardwood forest in central Vermont.
Bulletin of Torrey Botanical Club 91:455-465.
Bray, J. R. and Curtis, J. T. 1957. An ordination of the upland forest communities of southern Wisconsin.
Ecological Monographs 27:325-349.
Caplenor, D. 1968. Forest composition on loessal and non-loessal soils in West-Central Mississipi. Ecology
49:322-331.
Ezealor, A. U. 2002.Critical sites for biodiversity conservation in Nigeria. Nigerian Conservation Foundation,
Lagos. 110p
Chapman, J. D. and Chapman, H. M. 2001.The forests of Taraba and Adamawa States, Nigeria. An ecological
account and plant species checklist. University of Canterbury, Christchurch. New Zealand.
Dowsett-Lemaire, F. 1989. Physiography and vegetation of highland forests of eastern Nigeria.Tauraco Research
Report 1: 6-12.
Fishpool, L. D. C. 1997. Important Bird Areas in Africa. IBA criteria categories, species lists and population
thresholds. Birdlife International, Cambridge.
Ihuma, J, Chiuma, U. D. and Chapman, H. M. 2010. Tree species diversity in a Nigerian montane
forest ecosystem and adjacent fragmented forests. ARPN Journal of Agricultural and Biological Science 6(2):
17-22.
Mueller-Dombois, D and Ellenberg, H. 1964. Aims and methods of vegetation ecology.John Wiley and Sons Inc.
New York.547p
Obot, E. A. 1991. The savannah woodlands of Kainji Lake National Park, Nigeria. Diversity, regeneration and
size-class distribution. Discovery and Innovation 3:45-51
Skarpe, C. 1990. Shrub layer dynamics under different herbivore densities in an arid savanna, Botswana. Journal
of Applied Ecology 28: 873-885.
White, F. 1983. The vegetation of Africa. UNESCO, Paris.

125
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Vegetation analysis of ngel nyaki forest reserve, mambilla plateau, nigeria

  • 1. Journal of Natural Sciences Research ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online) Vol.3, No.12, 2013 www.iiste.org Vegetation Analysis of Ngel Nyaki Forest Reserve, Mambilla Plateau, Nigeria Aderopo Akinsoji Department Of Botany, University Of Lagos. Email: aderopoakinsoji@yahoo.com Abstract The vegetation of Ngel Nyaki Forest Reserve, Nigeria was analysed using data gathered with point-centred quarter method. 80 trees belonging to 29 species distributed in 21 families were encountered. The density of trees was 785 trees per hectare. The girth-size distribution curve indicated that the vegetation of Ngel Nyaki is stable and self-sustaining. The more dominant species based on Importance Values are Poulteria altissima, Polyscias fulva, Carapa grandiflora and Entandrophragma angolense. The least dominant species are Dombeya ledermanii, Celtis occidentalis and Croton macrostachyus. Keywords: Ngel Nyaki Forest Reserve, Mambilla Plateau, vegetation analysis 1. Introduction The forests of Nigeria form part of the Guinean forest biodiversity hotspot which extends from Sierra Leone to Cameroon mountains. The Cameroon highlands are fragmented and extends to eastern parts of Nigeria where they form montane and sub-montane forests. One of such fragmented forests is Nge lNyaki Forest Reserve (NNFR) which was gazetted as a forest reserve in 1969. NNFR which is located on the western escarpment of Mambilla Plateau in the south eastern corner of Taraba State, Nigeria at an altitude of 1450-1600m asl is a mosaic of mountain top grassland and sub-montane closed canopy forest limited to the streams’ valleys (Fig. 1). NNFR (07o 141 N 11o 041 E) covers an area of about 46km2 with a woody plant density of 669/ha (Ihuma et al, 2011). NNFR is one of the most floristically diverse montane –submontane forest stands in Nigeria (DowsettLemaire, 1989) and the most diverse on Mambilla plateau (Chapman and Chapman, 2001). It contains many plants which are endemic to the afromontane region of White (1983). This high level of endemism makes the forest a priority for conservation (Fishpool, 1997). NNFR has more than 146 vascular plants out of which 25 are in the IUCN Red Data List (Borokini et al., 2012) four of which are endangered and several are new to Nigeria (eg. Anthonotha noldeana) (Chapman and Chapman, 2001). The forest is also rich in birdlife (Ihuma et al, 2011) and has been classified as an Important Bird Area by Birdlife International and a critical site for biodiversity conservation (Ezealor, 2002). The climate is seasonal with dry season lasting from November to March and rainy season from April to October with a mean annual rainfall of 1780mm (Chapman and Chapman, 2001). The need to compare vegetation from different locations requires objective analysis of quantitative data. Akinsoji et al, (2003) stated that quantitative data obtained from objective sampling procedures is required for comparative purposes.Two methods used in gathering vegetation data are Count Plot methods (quadrats) and Plotless methods, also called Wisconsin Distance Methods (Mueller-Dombois and Ellenberg, 1974). Plotless methods are preferred because they are less laborious and time conserving. Of the four plotless techniques the one found to be most efficient is the point-centred quarter method (Cottam and Curtis, 1956). It has been widely used with satisfactory report in North America ( Caplenor, 1968, Boorman and Buell, 1964; Bray and Curtis, 1957) and in Nigeria (Akinsoji et al, 2003). Ngel Nyaki Forest Reserve is a fertile ground for research in tropical biology and conservation because of its diversity and level of endemism. The Nigerian Montane Forest Project has pioneered the research in NNFR and contributed immensely to literature. This study which is a phytosociological analysis of the sub-montane forest using point-centred quarter method is to complement the work done so far in NNFR. 2. Materials And Methods. At each sampling station, a baseline was established parallel to the forest edge. A transect perpendicular to the baseline was also established and a sampling point was located at a distance determined by a figure from random table. At each sampling point, four quarters were marked with the sampling point as the origin. The nearest tree to the origin in each quarter was identified. Its distance from the origin was recorded and its girth at breast height was also recorded. This procedure was carried out at 20 randomly selected points in the forest reserve. The few species that could not be identified in the field were taken to Forestry Research Institute Herbarium at Ibadan. All the distances were added together and a mean distance (d) was calculated. The mean area was computed as d2.. Using this value, the absolute density of trees per hectare was calculated as 10,000/d2. From this the absolute densities of each species was calculated and then relative densities. Frequency was calculated as the number of sampling points a species occurred divided by the total number of sampling points. Species dominance was calculated as basal area of a species divided by the total number of all species. Basal area (A) 121
  • 2. Journal of Natural Sciences Research ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online) Vol.3, No.12, 2013 www.iiste.org was calculated as A= c2 / 4.pi where c circumference and pi = 3.14. Relative frequency and relative dominance of each species was calculated. The three relative values were added together to obtain Importance Values (IV) for the species and they were ranked according to the magnitude of their IV. Fig. 1: Map of Southeastern Taraba State Showing Ngel Nyaki Forest Reserve. 3. Results and Discussion The forest is a closed canopy forest with gaps in places where there had been tree falls. A total of eighty trees belonging to twenty nine species distributed in twenty one families were recorded (Table 1). Most of the forest is relatively undisturbed but the edges are subjected to burning by incursions of grass land fires. Although the density of the forest trees was estimated to be 785 trees per hectare which is higher than the estimate of Ihuma et al, (2011), the actual density may be higher because the point-centred quarter method is known to underestimate absolute density of trees (Akinsoji et al., 2003, Skarpe, 1990) and species richness thus rarer species tend to be missed out. The girth size distribution 122
  • 3. Journal of Natural Sciences Research ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online) Vol.3, No.12, 2013 www.iiste.org Table 1. Tree Species Composition Of Ngel Nyaki Forest Reserve Sampled With Point-Centred Quarter Method. SPECIES Anthonotha noldeae Beilshmeidea mannii Carapa grandiflora Celtis occidentalis Chrysophyllum albidum Croton macrostachyus Deinbolia pinnata Diospyros montbutensis Dombeya ledermanni Entandrophragma angolense Ficus sp. Garcinia smeathmeanii Isolona deightonii Khaya grandifoliola Leptaulus zenkeri Macaranga occidentalis Oxyanthus speciosus Pleiocarpa pycnantha Polyscias fulva Poulteria altissima Pterygota mildbraedii Santiria trimera Strombosia schefflerii Symphonia globulifera Syzygium guineense Tabernaemontana contorta Treculia obovoidea Trichilia prieuriana Zanthxylum zanthxyloides FAMILY Leguminosae-Caesalpinoideae Lauraceae Meliaceae Ulmaceae Sapotaceae Euphorbiaceae Sapindaceae Ebenaceae Sterculiaceae Meliaceae Moraceae Clusiaceae Annonaceae Meliaceae Icacinaceae Euphorbiaceae Rubiaceae Apocynaceae Araliaceae Sapotaceae Sterculiaceae Burseraceae Olacaceae Clusiaceae Myrtaceae Apocynaceae Moraceae Meliaceae Rutaceae of trees (Fig. 2) shows that more of the trees fall within the smaller girth size classes and typifies the Type 1 curve of Obot (1991) which represents a stable self –sustaining plant population. There is more of smaller trees to replace the more mature trees when they reach senescence. The phytosociological analyses of NNFR are summarized in Table 2. Because of the underestimation of tree density and species richness due to the methods, relative values are employed to determine Importance values of species as an indicator of their dominance status in the community. The more dominant species in order of IV rankings are Poulteria altissima, Polyscias fulva, Carapa grandiflora and Entandrophragma angolense. Although P. altissima has low density and frequency values, but its large dominance value accounts for its overall dominance. The least dominant species are Dombeya ledermanni, Celtis occidentalis. and Croton macrostachyus. Their density, frequency and dominance values were comparatively small. 123
  • 4. Journal of Natural Sciences Research ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online) Vol.3, No.12, 2013 www.iiste.org 35 Number of trees 30 25 20 15 No of trees 10 5 0 0-20 21-40 41-60 61-80 81-100 >-9 Girth Size Class (cm) Fig. 2: Girth Size Distribution of Trees In Ngel Nyaki Forest Reserve. Table 2. Phytosociological Analyses Of Data Collected From Ngel Nyaki Forest Reserve SPECIES Poulteria altissima Polyscias fulva Carapa grandiflora Entandrophragma angolense Garcinia smeathmeanii Trichilia prieuriana Ficus sp. Anthonotha noldea Syzygium guineense Pleiocarpa pycnantha Macaranga occidentalis Strombisia scheffleri Oxyanthus speciosus Deinbollia pinnata Tabernaemontana contorta Leptaulus zenkeri Chrysophyllum albidum Khaya grandifoliola Diospyros montbutensis Beilshmiedia manni Isolona deightonii Zanthoxylum zanthoxyloides Treculia obovoides Pterygota mildbraedii Santiria trimera Symphonia globulifera Dombeya ledermanii Celtis occidentalis Croton macrostachyus *RDe 2.5 6.2 6.2 3.8 7.5 7.5 5 3.8 3.8 5 5 5 3.8 3.8 3.8 3.8 2.5 2.5 2.5 2.5 2.5 2.5 1.2 1.2 1.2 1.2 1.2 1.2 1.2 124 *RF 2.9 7.1 5.7 2.9 7.1 7.1 4.3 4.3 4.3 5.7 4.3 2.9 4.3 4.3 2.9 2.9 2.9 2.9 2.9 2.9 1.4 1.4 2.4 1.4 1.4 1.4 1.4 1.4 1.4 *RDo 17.3 6.8 7.1 11.6 3.6 3.6 4.9 5.9 4.9 2 2.1 3.1 2.7 1.5 2.1 1.9 2.2 2.2 1.3 1.3 1.2 0.9 1.9 1.8 1.7 1 0.89 0.89 0.5 *IV 22.7 20.1 19 18.3 18.2 18.2 14.2 14 13 12.7 11.4 11 10.8 9.6 8.8 8.6 7.6 7.6 6.7 6.7 5.1 4.8 4.5 4.4 4.3 3.6 3.5 3.5 3.1
  • 5. Journal of Natural Sciences Research ISSN 2224-3186 (Paper) ISSN 2225-0921 (Online) Vol.3, No.12, 2013 • • • • www.iiste.org RDe- Relative Density RF - Relative Frequency RDo-Relative Dominance IV - Importance Value 4. Acknowledgement I thank the Nigerian Montane Forest Project for permission to work in Ngel Nyaki Forest Reserve, Sikiru Kadiri and Saidu Mayosabere for field assistance and the entire Yelwa community. Dr. Tope Adeyemi prepared the figures. This study was funded by University of Lagos Central Research grant M2010/07. References. Akinsoji, A., Ayanbamiji, T, and Durugbo, E. U. 2003. Comparative phytosociological analysis in the GashakaGumti National Park using point-centred quarter and quadrat methods. Nigerian Journal of Botany 16:133-143. Borokini, T.I., Babalola, F. D., Amusa, T. O., Ivande, S. T., Wala, Z. J., Jegede, O. O., Tanko, D. and Ihuma, J. O. 2012. Community-based forest resources management in Nigeria: Case study of Ngel Nyaki Forest Reserve, Mambilla Plateau, Taraba State, Nigeria. Journal of Tropical Forestry and Environment 2(1):69-76. Boorman, F. H. and Buell, M.F. 1964. Old-age stand of hemlock-northern hardwood forest in central Vermont. Bulletin of Torrey Botanical Club 91:455-465. Bray, J. R. and Curtis, J. T. 1957. An ordination of the upland forest communities of southern Wisconsin. Ecological Monographs 27:325-349. Caplenor, D. 1968. Forest composition on loessal and non-loessal soils in West-Central Mississipi. Ecology 49:322-331. Ezealor, A. U. 2002.Critical sites for biodiversity conservation in Nigeria. Nigerian Conservation Foundation, Lagos. 110p Chapman, J. D. and Chapman, H. M. 2001.The forests of Taraba and Adamawa States, Nigeria. An ecological account and plant species checklist. University of Canterbury, Christchurch. New Zealand. Dowsett-Lemaire, F. 1989. Physiography and vegetation of highland forests of eastern Nigeria.Tauraco Research Report 1: 6-12. Fishpool, L. D. C. 1997. Important Bird Areas in Africa. IBA criteria categories, species lists and population thresholds. Birdlife International, Cambridge. Ihuma, J, Chiuma, U. D. and Chapman, H. M. 2010. Tree species diversity in a Nigerian montane forest ecosystem and adjacent fragmented forests. ARPN Journal of Agricultural and Biological Science 6(2): 17-22. Mueller-Dombois, D and Ellenberg, H. 1964. Aims and methods of vegetation ecology.John Wiley and Sons Inc. New York.547p Obot, E. A. 1991. The savannah woodlands of Kainji Lake National Park, Nigeria. Diversity, regeneration and size-class distribution. Discovery and Innovation 3:45-51 Skarpe, C. 1990. Shrub layer dynamics under different herbivore densities in an arid savanna, Botswana. Journal of Applied Ecology 28: 873-885. White, F. 1983. The vegetation of Africa. UNESCO, Paris. 125
  • 6. This academic article was published by The International Institute for Science, Technology and Education (IISTE). The IISTE is a pioneer in the Open Access Publishing service based in the U.S. and Europe. The aim of the institute is Accelerating Global Knowledge Sharing. More information about the publisher can be found in the IISTE’s homepage: http://www.iiste.org CALL FOR JOURNAL PAPERS The IISTE is currently hosting more than 30 peer-reviewed academic journals and collaborating with academic institutions around the world. There’s no deadline for submission. Prospective authors of IISTE journals can find the submission instruction on the following page: http://www.iiste.org/journals/ The IISTE editorial team promises to the review and publish all the qualified submissions in a fast manner. All the journals articles are available online to the readers all over the world without financial, legal, or technical barriers other than those inseparable from gaining access to the internet itself. Printed version of the journals is also available upon request of readers and authors. MORE RESOURCES Book publication information: http://www.iiste.org/book/ Recent conferences: http://www.iiste.org/conference/ IISTE Knowledge Sharing Partners EBSCO, Index Copernicus, Ulrich's Periodicals Directory, JournalTOCS, PKP Open Archives Harvester, Bielefeld Academic Search Engine, Elektronische Zeitschriftenbibliothek EZB, Open J-Gate, OCLC WorldCat, Universe Digtial Library , NewJour, Google Scholar