STUDIES ON THE MORPHOLOGY PHENOLOGY  AND  SEED GERMINATION OF   PENTACLETHRA   MACROPHYLLA BENTH

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ABSTRACT

The morphology, phenology and seed germination  of the multipurpose African oil bean tree, Pentaclethra macrophylla Benth. belonging to the family Fabaceae were studied. The study area covered   the entire Nsukka zone of Enugu State, Nigeria, and the ten towns randomly selected included: Adani, Amalla Egazi, Ede Oballa, Eha Alumona,  Eha Amufu, Ibagwa,

Imilike, Nsukka, Ogrute and Orba. Morphological  aspects of the study included: the  bole type, branching pattern, leaf types, leaf arrangement and crown shape; height of the trees and girth of the bole at breast height; size of the leaves, raches and leaflets; thickness of  the bark, length of some of the buttress  roots and diameter of the roots 20 cm away  from the stem; type of inflorescence and flower, and morphology of pollen. The morphology of the seedling of P. macrophylla was studied and photographed from the onset of seed germination up to 40 days  after  germination.  The  phenological  aspects  of  the  species  studied  were  period  of flowering,  fruiting,  leaf fall (defoliation)  and  replacement  (refoliation),  fruit maturity and ripening. The phenological observations were made every month for three years (2009, 2010 and 2011). There were two flowering periods of the species within a season (May to June and October  to  February).  Fruiting  took place  between  December  and the following  August. Defoliation  of  P.  macrophylla  trees  occurred  mainly  between  the  months  of  April  and September,  with  very  negligible  percentage  in  the  rest  of  the  months.  Refoliation  was observed  from the month of October to March. Fruit maturation and seed dispersal in the locations sampled started in April and ended in November   in the three years of sampling. Seed   germination   was carried out to determine the effects of different types of media on seed germination and seedling growth of P. macrophylla. The media used were Garden soil (which served as control), saw dust (SD), 1:1 mixture of Saw dust and Garden soil (SD+GS),

1:1:1 mixture of Saw dust, Garden soil and Poultry droppings (SD+GS+PD), 1:1 mixture of Garden soil and Poultry droppings (GS+PD), 1:1 mixture of Saw dust and Poultry droppings (SD+PD). The  highest percentage germination response was obtained using SD+GS+PD and GS+PD respectively which differed significantly (P<0.05) from  SD+PD, SD and SD+GS. The results of the effects of mechanical scarification on the  germination of oil bean seeds showed that there was remarkable improvement in the germination rate of the seeds scarified mechanically with sand paper and on rough cement floor at both the micropylar and stylar ends. The seeds scarified at the stylar end on rough  cement floor began germinating 11 days after sowing while the control started germinating on the 16th day after sowing with a peak on the 19th day. The association between tree phenology, temperature and rainfall reinforces the evidence for potential effects of changes in climate on P. macrophylla and probably other species of the Tropical Rainforest.

Chapter one

1.0   Introduction

1.1     Background to the study

The earth’s vegetation is very rich in diverse phytobiota that sustains man and his livestock. Man’s dependence  on plants dates back to man’s origin.  Of all the  vegetations,  tropical rainforests have been reported to contain the greatest number of various types of plant species (Nzekwe  et  al.,1993;  Singh,  2004;  Gurevitch  et  al.,  2002).  Singh    (2004)  reported  that tropical rainforests occupy about 8% of the earth’s  surface. Of all the tropical rainforests, those in the developing countries have been reported to be the reservoir of plant bioresources, and contain about 60-90% of the total number of plants on earth (Isichei, 2005). Man depends on plants for his   diverse  food  requirements  either directly or indirectly.  Okafor   (1983) reported that man obtains food from plants in the form of grains, stem and root tubers, seeds, nuts, fruits and leafy vegetables among others.

Numerous authors have reported that plants constitute the major sources of man’s industrial raw material (Okafor, 1981; Okafor, 1983; Isichei, 2005; Okojie,1993).  Apart from food and industrial raw materials, several reports have revealed that man obtains herbal drugs, dyes, spices and other numerous resources from plants for his well being as well as other socio- economic reasons ( Okafor, 1981; Sofowora,1982; Mendelson and Black, 1995; Okafor and Ham,  1999;  Anon,  2005).  Despite  the  indispensable  roles  plants  play  in  man’s  socio- economy,  reports  have  shown  that  the  forests  that  habour  the  plants  are  being  rapidly depleted (Nzekwe et al.,1993). Depletion of the forests, particularly, tropical rainforests has been  globally  associated   with  various   factors   of  which   increase   in  population   and advancement in technology are prominent.

Several  ecologists  have  given  insight  on  the  rate  of  depletion  of  the  world’s  tropical rainforest and its endangered status. Nzekwe et al.(1993) reported that about twenty million hectares of land are lost annually in the world as a result of anthropogenic activities. Anyiam (1995) reported that in the 1950’s, about 40% of the earth’s surface  was occupied by the tropical rainforests, and by 1975, the forested area was reduced to about 15%. Wilson (1992) pointed out that progressive depletion of the tropical rainforests has reduced it to 10%. Many environmentalists have shown that Africa alone has lost about 65% of her original rainforests, while Central America and Asia have lost  about 66% of theirs (Wilson, 1992; Nzekwe et al.,1993;  Mendelson and Black, 1995).  Wilson (1992)  pointed  out that if the rate of the depletion of the rainforests continues,  it could result in their disappearance in about 25-30 years time.

Similar alarm was also raised by Sayer and Whitemore (1991) about the depletion of  the tropical rainforests. The authors pointed out that if the depletion of the tropical rainforests is not put on check, most plant species as well as animals would be driven into extinction in about 30 years time. The authors further pointed out that the  disappearance of the tropical rainforest would be a great global setback in the  availability of biodiversity. According to them, Nigeria is among the twelve nations whose deforestation rate accounts for about 80% of the global total. With the recent climate change and its effects on the vegetation and the ongoing  deforestation,  it  is  likely  that  more  hectares  of  the  tropical  rainforest  would disappear.

1.2   Deforestation of Nigeria’s tropical rainforests

Okafor    and    Ham    (1999),    Okali    (2004)    and    Isichei    (2005)    observed     that depletion/deforestation of Nigeria’s tropical rainforest mainly located in the southern states of the country was caused by human activities. The authors reported that lumbering is one of the factors responsible for the depletion of the tropical rainforests in Nigeria. They posited that most people  cut  down trees for  timber  indiscriminately  without    replanting  and  without regard to the age of the trees. According to the authors (Okafor and Ham, 1999; Okali, 2004; and Isichei, 2005),when the trees are felled, other  non-timber species are destroyed in the process  of logging especially during felling  of  the trees and clearing of the area for the sawing of the logs into sizes.

Nzekwe   (2002)   reported   that   slash   and   burn   agricultural   practices;   indiscriminate establishment of industries, tertiary institutions, filling stations, state and  local government area headquarters hospitals, railway, airports and other business centres exert pressure on the tropical rainforest of Nigeria. Okafor (1983) reported that forest fires strongly attack tropical rainforests as such fires spread to other places not targeted for burning. The author noted that forest fire kills off plants, especially shrubs that stand well above the ground. He also noted that  forest  burning  exposes  the soil to  erosion  which  is acknowledged  nationwide  to be common in the tropical rainforest zones of Nigeria. Forest fire has been identified to destroy seed bank, delay regeneration and reproduction in plants, as well as kill off non fire resistant plant species (Okojie, 1995;  Okali 2004). Keay (1989)  and Nzekwe (2002) reported  that constant fire outbreak in the tropical rainforest which always occurs in the dry season, results in retrogressive  succession,  hence converting  tropical  rainforests  to savanna  woodland  or

derived savanna forest as exemplified by most vegetations of Enugu and Anambra States of

Nigeria.

1.3   Statement of the Problem

There is no doubt that forest is vital to man’s socio-economic  survival. Emphasizing  the contribution of the forests and their resources to man’s economy, Wilson (1992) described the forest as a vital source of new wealth and knowledge. Several other authors (Okafor,1983; Achinewhu et al., 1995) reported that the forest provides man with timber, food, shelter and different types of industrial raw materials. Most of the current orthodox drugs used in treating different  types  of  ailments  are  directly  or  indirectly  derived  from  plants  (Anon  2005; Kannaiyan, 2005;  Sofowora, 2008). Okorie et al. (2006) reported that more than one third of the modern drugs are derived from plant species of the Tropical Rainforest.

Okafor  and Ham  (1999)  in a summary of the importance  of tropical  rainforests  to  man reported that “by losing plants, we are losing our natural economic packages”. Conservation management and biotechnological exploitation of the resources of phytobiota in developed countries  have led to revolutionalised  agricultural,  industrial  and enterpreneural   activities that consequently caused a decrease in unemployment, increase in wealth and convergence of intellectual giants (Singh, 2004). Presently,  biotechnologically  processed products of these industrial countries now flood the  developing countries in different forms of herbal drugs, tea, soap, toothpaste etc. making the latter dumping grounds.

Following  the  current  events  in  the  developing  countries;  increased  population;  mass unemployment;  retrenchment/disengagement   of  healthy,  able  bodied  personnel;  hunger, poverty,  diverse  crime  waves,  climate  change-  influenced  vegetation  etc.,  it   becomes necessary that national income resources be diversified. In Nigeria, dependence on petroleum

products  as the main source of income  generation  should  not be relied  upon since  such reliance could create more problem than it could solve. Non-oil and non-timber  resources should be given priority attention. Nigeria, being the largest country in sub-Saharan Africa, has humid  tropical  rainforest  zones that are richly endowed  with  a lot of different  plant species  of economic  value. Though detailed  account  of the  economic  plants in Nigerian tropical rainforest zone is inadequate, it is necessary that those of ethnobotanical economic values be conserved for fuller biotechnological exploitation especially the indigenous species whose economic importance was not appreciated early (Okafor,1983). One of the indigenous plant species of Nigeria’s Rainforest zone that requires urgent attention for conservation is the  multipotential   African  oil  bean  tree,  Pentaclethra   macrophylla   Benth.(“Ukpaka”-

‘1bo’),which has been chosen as the main species for the present study. The species cannot be conserved without the full knowledge of its ecological requirements for establishment and survival. The plant is highly felled for fuel wood because of its hardwood yet the seeds are major sources of protein and other food nutrients.  Unfortunately,  conscious efforts are not made to replant it as it should probably because of its long gestation period. It is therefore necessary  to  understudy  the  plant  and  contribute  to  the  conservation  of  the  otherwise currently endangered species for future biotechnological exploitation.

Although African oil bean seed is a popular indigenous plant in many countries in the tropics, it  is  referred  to  as  underutilized  species  because  of  its  small  total  economic  value  in commercial production and trade compared  with other crops and  agricultural commodities (Akindahunsi,  2004;  Enujiugha  and  Akanbi,2005).  It  is  listed  among  other  crops  as  an underutilized plant (IPGRI, 2002; Jaenicke and Hoschle-Zeledon, 2006).

Underutilised  crops are those that  were once  grown more widely or intensively but  are falling  into  disuse  for  a  variety  of  agronomic,  genetic,  economic  and  cultural  reasons.

Farmers  and  consumers  are  using  these  crops  less  because  they  are  in  some  way  not competitive with other species in the same agricultural environment.  The decline  of these crops may erode the genetic base and prevent distinctive and valuable traits being used in crop adaptation and improvement (IPGRI, 2002).

1. 4       Aim and Objectives of the Study

The aim of the study was to investigate the morphology, phenology and seed germination of

P. macrophylla.

The specific objectives of this work were:

(i)        to ascertain the morphology of the seedling and the mature tree, (ii)        to determine the phenology of the plant, (iii)      to evaluate the effects of different media on its seed germination.



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