Floral Diversity of South-Western Nigeria Coastal Environments
Transcription
Floral Diversity of South-Western Nigeria Coastal Environments
Journal Sci. Res. Dev., 2008 / 2009, Vol. 11, 9 – 20 Floral Diversity of South-Western Nigeria Coastal Environments Olusola H. Adekanmbi,* Ogundipe O. T. and Olowokudejo J. D. Department of Botany and Microbiology, University of Lagos, Lagos, Nigeria. ABSTRACT Mangrove communities in 8 localities in Lagos State viz: Atlas Cove, 5 Cowrie Creek, Maroko, Berger De Motz, Palaver Island, Bayeku, Majidun, and University of Lagos Beach were sampled quantitatively with respect to their flora diversity. Absolute count and relative percentages of the vegetation were estimated. The first sampling site Atlas Cove has its vegetation relatively well preserved, 5 Cowrie is devoid of typical mangrove vegetation, Maroko swamp has been taken over by grasses, Berger De Motz has sandy substratum, high energy wave and rip of any typical mangrove species, Bayeku and Majidun still preserve the relics of their biodiversity, while mangrove is still relatively well preserved in the vicinity of University of Lagos lagoon and Palaver Island. The importance of having wetland reserves is highlighted. Key words: mangrove, degradation, natural environment, flora diversity, transect. INTRODUCTION The Nigerian coastline is made up of swampy ground separated by fresh or brackish lagoons and a network of creeks. The typical mangrove swamp forest develops on the muddy banks of these creeks where the water is brackish and the number of species is limited by their tolerance to specific environmental condition (Olowokudejo, 1975). The mangrove swamp forest typified by the Niger Delta is characterized by three species of Rhizophora, which are Rhizophora harrizoni, R, mangle and R. racemosa. Cohabiting with Rhizophora are two other less abundant mangroves, Avincennia germinans and Laguncularia racemosa as well as the salt-water fern, Acrostichum aureum (Sowunmi, 1981a & b). Behind the mangrove swamp is a zone of freshwater swamp inhabited by freshwater species such as Symphonia globulifera, Cleistopholis patens, Nymphae lotus, Ipomoea spp., Vossia cuspidata and other grasses. Also found in the freshwater zone are the floating communities of Pistia stratiotes, Lemna and Salvinia among others. Associated with the swamp vegetation, but by the edge mainly near the seaboard, where the seawater is undiluted is a strand vegetation of shrubs and herbs, such as Barteria nigritiana, Hibiscus tiliaceus, and Ipomoea pes-caprae (Keay, 1949; Lawson, 1966). Corresponding author. E-mail: [email protected] 10 Olusola H. A,* Ogundipe O. T. and Olowokudejo J. D. The mangrove forest occurs on muddy intertidal substrates, making it habitable for birds and other living organisms by stabilising the silt-rich soil and holding it together by a mat of mangrove rootlets forming a thick felt raft of peaty texture. The subsequent breaking down of the raft in addition to deposition of coarse detritus and of leafy woody material results in something nearly resembling a normal soil of the hinterland (Chapman, 1979; Tomlinson, 1986). In this way the mangrove forest advances slowly outward, leaving dry land behind. Mangroves are highly productive biotopes and as such, support a vibrant, rich and endemic wildlife that include the enormous variety of crabs, ducks, geese and immense varieties of sea life in the food webs (Odum and Herald, 1975; Nwafor, 2006). Wild birds also stop over at the mangroves during migration (Erarome, 2005). If properly managed, mangroves can provide timber for construction, charcoal for energy, food for livestock and fish for local consumption among others. This paper discusses the value of swamps, the peculiar flora species found in specific parts of the Lagos coastal area and importance of conserving these biodiversities. MATERIALS AND METHODS A comprehensive quantitative vegetation analysis of eight lagoonal communities: Palaver Island, Atlas Cove, 5 Cowrie creek, Maroko, Bayeku, Berger De Motz, University of Lagos Beach, and Majidun were carried out. Eight belt transects of 50 metres long and 6 metres wide placed at every fifth yard were examined for each sample site. A list of all the species present in each mangrove community was compiled. Species frequency was numerically estimated in 10 quadrats within these transects and the percentage of the total flora was calculated. Vegetation cover of species present in each transect was also estimated by assigning each species to one of six categories: Dominant - largest and most abundant sp., Very abundant with the greatest percentage cover but not ecologically dominating other plants, Abundant - numerous or widespread, Frequent -modest numbers but soon seen, Occassional -in small number and not found in all transects, Rare -found only singly and scarcely and absent from most samples following Killick, 1967. Visual photographs of the various mangrove communities were taken. RESULTS All plants species present at each sampling site, their frequency and the percentage occurrence are presented in Tables 1. Table 2 and 3 shows a list of woody and herbaceous species common to five or six localities. A total of 56 plant species analogue to 29 families were recorded for all the 8 sampled vegetation communities. Visual photographs of some of the sampled communities are shown in Plate 1-6. Floral Diversity of South-Western Nigeria Coaster Environments 11 Vegetation Description Atlas Cove Mangrove here is relatively well preserved dominated by Avicennia germinans (6.9%) and Laguncularia racemosa (6.3%). Rhizophora racemosa (5.9%) and Alchornea cordifolia (5.6%) were very abundant occurring in an almost undisturbed manner. Casuarina equisetifolia (2.5%) and Terminalia catappa (1%) were other abundant tree species recorded in this mangrove community. Occurring frequently were shrubs such as Agave sisalana (3.8%), Dalbergia ecastaphyllum (2.7%), Drepanocarpus lunatus (2%) and the fern Acrostichum aureum (2.8%). Phoenix reclinata (2.1%), Cocos nucifera (1.8%), Azadiracta indica (1.4%) and Hibiscus tiliaceus (1.1%) were found occurring together occasionally. Paspalum vaginatum (9.1%), Portulacaceae (8.8%) and Rhynchospora corymbosa (2.1%) were abundant. 5 Cowrie Creek This community is almost completely devoid of vegetation except occasional stands of Casuarina equisetifolia (7.89%), Terminalia catappa (5.26%), and sparse occurrence of grasses. Chromolina odorata (7.89%) were frequent. The indiscriminate cutting, grazing and sand filing has obliterated any sign of the original mangrove vegetation. 12 Olusola H. A,* Ogundipe O. T. and Olowokudejo J. D. 3 4 5 6 7 8 9 3 8 42 48 33 Rhizophoraceae 47 52 43 Euphorbiaceae Combretace ae Casuarinaceae 40 7 18 Malvaceae Fabanaceae 8 19 Fabanaceae 14 Adiantaceae Aracaceae Aracaceae Meliaceae Agaveceae Pontedereriaceae Nymphaceae Aracaceae Poaceae Portulacaceae Cyperaceae 20 13 15 10 27 Aracaceae Compositae Combretace ae Poaceae 12 16 22 49 8 12 8 13 4 26 M a ji d u n co m m u ni ty % U n i ve rs i ty o f L a go s % Be rg e r D e m o tz % M o b a, M a ro k o % 0.00 0.00 5.00 13.33 0.00 6.67 0.00 0.00 32.21 22.15 17.45 0.00 T ot al 5 c o w ri e c re ek % 0.00 0.00 At la s C o ve % 75.00 28.19 40 58 240 19.58 0.00 0.00 0.00 21.67 17.92 16.67 24.17 28 5 103 34 70 38.83 20.59 25.71 0.00 23.53 17.14 0.00 23.53 18.57 0.00 17.65 0.00 0.00 0.00 10.00 0.00 0.00 0.00 33.98 0.00 28.57 27.18 14.71 0.00 8 100.00 77 24.68 0.00 0.00 0.00 0.00 0.00 0.00 0.00 32.47 0.00 23.38 0.00 19.48 0.00 0.00 20 25 18 15 19 12 8 5 12 38 49 4 29 15 13 11 32 64 48 46 34 15 60 149 35 6 7 M aj i d u n c o m m u n i ty Ba ye ku 45 Avicenniaceae U ni v er si ty o f La g o s P al a ve r s ou t h M o b a , M a ro k o B er g er D e m o tz A tl as Co v e Taxa Combretace ae B ay ek u % 2 racemosa Avicennia germinans. Rhizo phora racemosa Alchorn ea cordifo lia Terminalia ca ta ppa Ca suarina equisetifolia Hib iscus tiliaceus, Dalbergia ecastaphyllum Drepano ca pus P a la v er s o u th % Species 1 Laguncularia 5 co w r ie cr ee k V e g e tat io n C om m i n iti e s Table 1: showing the complete floristic list and vegetation taxa with its vegetation percentages 23.33 0.00 0.00 25.00 0.00 0.00 31.67 20.00 127 15.75 18 72.22 48 31.25 19 52.63 27 100.00 94 0.00 61 0.00 57 0.00 302 21.52 63 100.00 55 27.27 60 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 12.58 0.00 0.00 0.00 0.00 0.00 47.37 0.00 0.00 0.00 0.00 19.87 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 13.91 0.00 45.45 6.30 27.78 0.00 0.00 0.00 0.00 0.00 0.00 3.97 0.00 0.00 9.45 0.00 0.00 0.00 0.00 15.96 0.00 0.00 6.29 0.00 0.00 29.92 0.00 8.33 0.00 0.00 15.96 21.31 19.30 10.60 0.00 27.27 38.58 0.00 60.42 0.00 0.00 68.09 78.69 80.70 11.26 0.00 0.00 12 100.00 56 28.57 22 100.00 155 31.61 0.00 21.43 0.00 20.00 0.00 17.86 0.00 23.23 0.00 0.00 0.00 25.16 0.00 7.14 0.00 0.00 0.00 0.00 0.00 0.00 0.00 10.71 0.00 0.00 0.00 14.29 0.00 0.00 lunatus 10 11 12 13 14 15 16 17 18 20 21 22 23 24 25 26 27 28 29 30 31 32 34 35 36 37 38 40 41 42 43 44 45 46 47 48 49 Acrostichu m aureum Co co s nucifera Phoenix reclina ta Aza diracta indica Agave sisa la na Eicch ornia cra ssip es Nymphae lotus Pistia stra tiotes Paspalum vag in atu m Portu la ca cea e Rhynchospora corymbosa. Elais guinensis Ch rom olin a o dorata Combretum sp Paspalum scrob iculatum Panicum subalbidum Andropogo n sp. Asystasia gang en tica Typha au stra lis Scleria depressa Kyllin ga erecta Cyperus esculentus Centro sem a pubesens Ipo moea aqu atica Saccha rum officinaru m Symphon ia globulifera Alstonia co ngensis Cyperus javanicus Vossia cuspidate Bambusa vu lg aris Luffa cylin drical Mimosa invisa Poaceae Raph ia finifera Ludwigia sp . Willo w p la nt Cytosperm a sensgalense 9 15 65 63 15 38 60 42 12 25 12 10 31 36 19 15 4 6 8 39 45 53 Poaceae Poaceae Acantaceae Typhaceae Cyperaceae Cyperaceae Cyperaceae Papilionaceae 38 65 33 39 24 39 21 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.00 100.00 100.00 100.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 35.56 62.50 0.00 37.50 16 5 3 45 8 0.00 0.00 0.00 0.00 0.00 0.00 46.67 0.00 17.78 0.00 0.00 0.00 Guttiferae 6 2 8 0.00 0.00 0.00 0.00 0.00 0.00 75.00 25.00 Apocynaceae Apocynaceae Cyperaceae Poaceae Poaceae Mimosaceae Poaceae Aracaceae Onagraceae 7 7 80 87 17 36 35 39 26 36 26 39 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 43.59 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 56.41 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 33.33 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.00 100.00 66.67 100.00 0.00 100.00 100.00 100.00 100.00 Convolvulaceae Poaceae 12 17 8 45 53 38 65 33 39 24 39 80 87 17 24 35 22 26 36 26 39 Floral Diversity of South-Western Nigeria Coaster Environments 13 Table 2: Woody Species Common to Five or More Localities 1. 2. 3. 4. 5. 6. 7. 8. Species Family Habit Laguncularia racemosa Terminalia catappa Linn Casuarina equisetifolia Linn Cocos nucifera Azadiracta indica A. Juss Avicennia germinans Conocarpus erectus Rhizophora racemosa G.F.W. Mey Combretaceae Combretaceae Casuarinaceae Aracaceae Meliaceae Combretaceae Combretaceae Rhizophoraceae Tree Tree Tree Tree Tree Tree Woody Woody Table 3: Herbaceous Species, Climbers and Grasses Common to Five or More Localities 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. Species Family Habit Phoenix reclinata Chromolina odorata Linn Mimosa invisa Mart Chromolina odorata Linn, King & Robinson Mart Conocarpus erectus Paspalum vaginatum Sw Paspalum scrobitulatum Linn Andropogun sp Panicum subalbidum Kunth Scleria depressa Willd Paspalum vaginatum Scleria depressa Willd Aracaceae Compositae Mimosaceae Herbaceous Herbaceous Herbaceous Compositae Cucurbitaceae Poaceae Poceae Poaceae Poaceae Cyperaceae Cyperaceae Cyperaceae Herbaceous Shrub Grass Grass Grass Grass Sedge Sedge Sedge Moba, Maroko Swamp This swamp community has been taken over by grasses due to urbanization and reclamation. As a result grasses such as Paspalum (25%) and Andropogon (22%) species were found dominating. Panicum subalbidum (1.9%) were very abundant reaching about eight feet high. Tree species occurring frequently are Casuarina equisetifolia (5.4%), Azadiracta indica (3.8%), and Terminalia catappa (3.3%). 14 Olusola H. A,* Ogundipe O. T. and Olowokudejo J. D. Berger De Motz This community has sandy substratum and high-energy wave. It is rip of any typical mangrove species as the natural environment has been adversely modified. Grasses including Typha australi (11%), Paspalum and sedges such as Kyllinga erecta (6.7%), Scleria depressa (5.7%), Rhynchospora corymbosa (4.3%) and Cyperus esculentus (4.1%) are dominant here. Very abundant are Centrosema pubesens (6.7%) and Asystasia gangetica (6.5%). Drepanocarpus lunatus (2.6%) and Ipomoea aquatica (2.1%) are also abundant. Palaver Island This community is relatively undisturbed by developers except the influx of solid waste. Rhizophora racemosa (19%) is found dominating; next to this in abundance are the very mature Avicennia germinans (17%) reaching about 5 feet in girth and about 50 feet in height. Dalbergia ecastaphyllum (8.9%) were quite abundant. The saltwater fern Acrostichum aureum (2.8%), Ipomoea aquatica (2.8%), Casuarina equisetifolia (2.5%) and Cocos nucifera (1.8%) are frequent. Bayeku Community The mangrove floral of this community is dominated by Rhizophora racemosa (13%). Very abundant is Avicennia germinans (10%) and Dalbergia ecastaphyllum (5.6%). Paspalum vaginatum (5.9%), Eicchornia crassipes (4%), Acrostichum aureum (3.7%) were frequently counted. Laguncularia racemosa (2.5%) recorded only occasional occurrence. Majidun Community Dominant in this fringing mangrove lining creeks with fresh water incursion are the sedges Vossia cuspidata (7.13%), Cyperus javanicus (0.98%) and Rhynchospora corymbosa (2.62%). Rhizophora racemosa (4.75%) is found occurring together with Alchornea cordifolia (2.29%) at some sampled sites. Very abundant here are, Nymphae lotus (8.03%), Eicchornia crassipes (6.88%), Pistia stratiotes (6.22%) and Acrostichum aureum (4.01%). Mimosa invisa (2.87%), Raphia finifera (2.13%) and Ludwigia species (2.95%) are abundant. Other frequently occurring species are Phoenix reclinata (2.38%), Ipomoe aquatica (1.64%), Paspalum scrobiculatum (1.64%), Bambusa vulgaris (1.39%), and Drepanocarpus lunatus (0.98%). Agave sisalana (0.82%), Terminalia catappa (0.41%) and Cocos nucifera (0.33%) are frequent. University of Lagos Community Mangrove in the vicinity of University of Lagos is still relatively well preserved with diverse species. A very visibly dominant species in this community is Rhizophora racemosa (6.8%), Salt water fern Acrostichum aureum (6.4%) is very abundant. Other important components of this community occurring in abundance are Alchornea cordifolia (5.9%), Avicennia germinans (4.4%), Casuarina equisetifolia (3.4%), Drepanocarpus lunatus (3.2%), Ipomoea aquatica (2.7%), and Dalbergia ecastaphyllum (2.5%). Paspalum vaginatum (5.4%), Pistia stratiotes (3.6%), Rhynchospora corymbosa (2.5%), as well as species of Agave sisalana (0.8%) and Floral Diversity of South-Western Nigeria Coaster Environments 15 Phoenix reclinata (0.7%) were frequently encountered in the samples. Tree species such as Alstonia congensis (1.2%), Symphonia globulifera (1%), and Terminalia catappa (0.3%), were occasionally seen. Eicchornia crassipes (2.5%) and Nymphae lotus (2.2%) recorded rare occurrence showing incursion of freshwater. Fig. 1: A Mangrove Habitat. Majidun, Lagos, Nigeria. 16 Olusola H. A,* Ogundipe O. T. and Olowokudejo J. D. Fig. 2: Hibiscus tiliaceaus (Malvaceae) . Atlas Cove, Nigeria. Fig. 3: Laguncularia racemosa (Combretaceae). Atlas Cove, Lagos. Nigeria. Floral Diversity of South-Western Nigeria Coaster Environments 17 Fig 4: Rhizophora racemosa (Rhizophoraceae) at low tide. Bayeku, Lagos. Nigeria. Fig. 5: Fringing mangroves lining creeks through fresh and salt water. Majidun, Lagos. Nigeria 18 Olusola H. A,* Ogundipe O. T. and Olowokudejo J. D. Fig. 6: Avicennia germinans (Avicenniaceae). University of Lagos, Lagos. Nigeria. DISCUSSION AND CONCLUSION The floristic list shows that the floral composition of the Lagos lagoon is diverse. On the sandy beaches are found plants like Elaeis guinnensis, Casuarina equisetifolia, Terminalia catappa, Hibiscus tiliaceus among others. Towards the sea, on shallow shore, there are submerged grasses with scattered mangrove seedlings in the shallowest parts. Much of the southwestern Nigerian coast is made up of the open type lagoon and its therefore influenced by the tide. The typical mangrove species such as Rhizophora racemosa, Avicennia germinans and Laguncularia racemosa are well represented. These species typical of the mangrove are found relatively well preserved at Atlas Cove, Bayeku, Majidun, University of Lagos and Palaver Island vegetation communities. The remaining sampled sites 5 Cowrie Creek, Maroko and Berger De Motz are completely devoid of typical swamp flora but replaced by occasional stands of Terminalia catappa, Casuarina equisetifolia, and grasses due to urbanization and reclamation. The largest mangrove stand in Nigeria is found in the Niger Delta and this work has established that the Lagos lagoon swamp flora communities are comparable to that of the Niger Delta. The coastal vegetation performs many important ecological roles. It filters nutrients, stabilize lagoon shores, provide protection for commercially important fish, help in the continuous formation of soil, and serve as an important migratory point for birds. The coastal vegetation protects the shoreline from being Floral Diversity of South-Western Nigeria Coaster Environments 19 washed away in storms. The roots and trunks break the force of the waves, and the leaves and branches reduce the effects of the wind and rain (UNESCO, 1992). The trees species of the mangrove are useful, for example mangrove wood is often collected as firewood, the willow plant is used in crafting furniture and other household amenities, and many plants of the mangrove have medicinal uses. The coast around the southwestern part of Nigeria constitutes one of the most fascinating resources in tropical Africa and it indeed is a center of biodiversity (Plate 1-6) (FAO, 2001). It is therefore recommended that some portions of the studied wetlands where typical wetland flora are well preserved and yet undisturbed be prepared and conserved as reserves. 20 Olusola H. A,* Ogundipe O. T. and Olowokudejo J. D. REFERENCES Chapman, V. J. (1979). The Place of Mangrove Vegetation in the Coastal Zone. In : Proceedings 7. Coastal zone Workshop of Environmental Centre, Canterbury Inc. Erarome, M. A. (2005). Nigeria: Country Pasture/ Forage Resources Profiles. University Press, Oxford. 52pp. Food and Agricultural Organization (2001). National Programme to Combat Desertification. University Press, Oxford. 50pp. Keay (1949). An Outline of Nigeria Vegetation. Federal Department of Forestry Research. 46pp. Killick, H. J. (1967). Beginning ecology. Ibadan University Press.121pp. Lawson, J. W. (1966). Plant life in West Africa. Oxford University Press. 147pp Nwafor, J. C. (2006). Environmental Impact Assessment For Sustainable Development. The Nigerian Perspective. Environmental and Development Policy Center for Africa (EDPCA). 658pp. Odum, W. E. and Herald, E. J. (1975). Mangrove forests and aquatic productivity :An Introduction to land water interactions. Springer-Verlag.136pp. Olowokudejo, J. D. (1975). Comparative morphological and anatomical studies Mangrove Swamp species. University of Lagos. 66pp. Tomlinson, P. B. (1986). The botany of mangroves. Cambridge University Press. 395pp. UNESCO. (1992). Environmental Education and information. Unesco/Unep. Sowunmi, M. A. (1981a). Late Quaternary Environmental changes in Nigeria. Pollen et Spores. 23: 125-148. Sowunmi, M. A. (1981b). Aspects of Late Quaternary vegetational changes. West African Journal of Biogeography. 8: 457-474. WWF., 1993. "Environmental Education: A background paper". A working paper developed by the Education sub-committee core group in Breaman Germany.
Similar documents
Cherry - Beech Creek Gardens
and the health of the environment are interdependent and that an understanding of nature improves the lives of individuals. We provide educational opportunities and interactive experiences that ins...
More informationChaparral 235 SSI, 2005 - RNR
NOTE: Numbers with letter designations represent parts included with primary numbered part for which there is no photo representation.
More information