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CHAPTER ONE


                                    INTRODUCTION


1.1    Background to the study

The growth of plants depends on the availability of nutrients from the soil. Thus, it is

important that the soil should potentially provide nutrients for the growth and development of

plants. Prolonged uptake of nutrients by growing plants depletes soil of vital nutrients,

adversely affecting the growth of plants. Organic manure can be added in order to

compensate for the losses due to leaching and uptake by existing plants from the soil

(Russell, 1998).

Milicia excelsa formerly called Chlorophora excelsa belongs to the family Moraceae. The

tree is mostly found in West, Central and East Africa, extending from Guinea Bissau to

Mozambique. Milicia excelsa is a durable wood used for the purposes of exterior and interior

joinery, frames and doors, luxury cabinet works and garden furniture. Other uses include

floorings, steps and stairs, paneling and moldings, decorative veneer, plywood and the

construction of vehicle and truck bodies (Oteng-Amoako, 2006). The high demand for the

wood and its other products has resulted in over exploitation.



The species is now considered as a scarlet species; these are species that are common but

under more imminent threat. Currently it has over 200 % exploitation rate by the Forestry

Department of Ghana and requires special permit for it to be harvested (The Ghana Forest

Service, 1998). To replenish the stocking of such valuable species, its plantations were

established. Seedlings of Milicia excelsa raised for plantation purposes appear weak and

slender in form and hardly withstand the adverse conditions of the weather making it very


                                               1
difficult in raising healthy seedlings and this affects the species growth performance as well

as its survival rate in the establishment of its plantation (Irvine, 1961).



Addition of poultry manure to improve the nutrient status of the growth medium (soil) can

enhance the general growth performance of seedlings in a nursery. The introduction of

Milicia excelsa into plantations could have beneficial effects on the forest of Ghana, since it

will reduce the high dependency on the forest for Milicia excelsa species for subsistence or

commercial purposes. However, for a plantation program to yield maximum environmental

and economic benefits, healthy and good seedlings should be supplied inexpensively

(Appiah, 1998).




1.2     The Problem statement

 Seedlings of Milicia excelsa raised for plantation purposes appear weak and slender in form

 and hardly withstand the adverse conditions of the weather making it very difficult in raising

 healthy seedlings and this affects the species growth performance as well as its survival rate

 in the establishment of its plantation (Irvine, 1961). There is therefore the need to investigate

 possible solutions to this problem in order to enhance the species growth performance.




1.3     Justification of the study

Manuring can help increase the nutrient status of soils depleted due to leaching and uptake by

existing plants from the soil. A lot of effort has been put into the promotion of the use of

mineral fertilizers for crop production, not much seems to have been done in the use of

organic forms of fertilization for soil fertility amelioration (MOFA, 1998).




                                                 2
The use of organic manure preferably, poultry manure will help and encourage the

establishments of Milicia excelsa plantations. This will facilitate increasing supply of Milicia

excelsa timber products in the world market.



1.4      Aim and objectives

This study aims at determining the effect of organic manure on the early growth performance

and the percentage survival of Milicia excelsa seedlings.


Specific objectives


      1. To determine the effect of poultry manure on the vegetative growth (stem height and

         diameter) of Milicia excelsa seedlings.

      2. To determine the effect of poultry manure on the percentage survival of Milicia

         excelsa seedlings.

      3. To determine the effect of poultry manure on the mean number of Milicia excelsa

         seedling leaves over some period of time.




1.5      The research hypothesis


The research null hypothesis was that poultry manure would not provide environmental

conditions favourable for the growth and development of Milicia excelsa seedlings. However,

the alternate hypothesis for this research was that different levels of poultry manure would

provide environmental conditions favourable for the growth, development and survival of

Milicia excelsa seedlings.




                                                   3
CHAPTER TWO


                                LITERATURE REVIEW


2.1    The Milicia Species


Milicia excelsa formerly known as Chlorophora excelsa and locally known as “Odum”

belongs to the family Moraceae. In Africa the genus Milicia, has two species, M. excelsa and

M. regia. The African species are very similar and are not distinguished in the timber trade,

but are commonly referred to as “Iroko” (Hawthorne, 1990). Milicia excelsa is currently

found in forests of Africa stretching across the West Africa sub- region from Senegal through

Cote D’ Ivoire, Ghana to Nigeria. Other places of occurrence include Angola, Mozambique

and Tanzania (Hall and Swaine, 1981). Guinko (1985) cited by Cobbinah (1992) speculated

that the presence of M. excelsa in fetish worship sites or on sites of former special cemeteries

is an indication that the species may have a wide distribution than its present range. The

Odum tree provides        hard, termite-resistant,    all-purpose wood      which is     highly

commercialized.




2.1.1 Botanical Description of Milicia excelsa


Odum is a very tall deciduous tree, which can grow to about 60 meters high and 2.5 meters in

diameter. It may have a straight cylindrical bole of about 30 meters before branching (FAO,

1986). However according to Brooks (1949), these dimension tend to be less in drier areas.

The buttress is usually short and blunt, sometimes with root spurs and large exposed reddish

brown lateral roots.




                                               4
In the young tree, the bark is smooth but later becomes rough and flaking. In the mature tree,

the rough bark has reddish-brown conspicuous lenticels and slashes very gritty with brown

spots and rapid watery latex. Venation on its lower surface looks like a sponge with

conspicuous gaps in between the veins with lateral nerves up to 12 in maximum with a simple

petiolate leaf (Hawthorne, 1990). The juvenile leaf is oblong-elliptic with serrate margin and

densely covered with hair below the leaf (FAO, 1986). It is usually light green, soft and

smooth to touch. However, as the tree grows, it puts on new leaves of different form – broad,

ovate with darker colouring and less serrated edges which are shiner (white, 1966).




2.1.2 Ecology of Milicia excelsa Seedlings


Milicia is a pioneer species. The seedling thus responds strongly to increase in irradiance. It

cannot survive in deep forest shade but grows rapidly in full sun. Photoblasticity in the

species accounts for its prevalence in more heavily disturbed forest, on road margins and on

farms. The seedling shows greater investments in leaves. When it happens to occur in the

under shade, it produces thin leaves with large surface area, while thick leaves are produced

in high irradiance, having lower specific area. It has high leaf turn over in all light intensities

(Swaine et al, 1997). Generally, it has high compensation and low saturation points.




The common adversary to the seedling is Phytolyma spp which cause galls to be formed on

the leaves. This disrupts the plants normal physiological processes, causing epical dieback,

growth reduction and seedling mortality. The succulent young shoots are sometimes browsed

by duikers and other animals (Irvine, 1961). The Milicia gall bug, Phytolyma spp are insects

of the order Homoptera and the family Psyllidae.



                                                5
2.2    Growth in Tropical Seedlings


A seedling is a plant in which a significant proportion of its biomass is constructed from seed

reserves, rather than from resources acquired auto-trophically (Kitajima, 1996). However, by

convention, a seedling to a forester refers to a young plant of about 2.7 m (Whitmore, 1996).

Seedlings are basically of two types, those that can do well under shade cover called shade

tolerant and those that can only survive and grow well in the presence of light, called shade

intolerant or pioneer species (Swaine et al, 1997).




The growth of a tropical tree seedling in a particular environment and their ability to adapt to

changes in that environment depend on the complex interaction of the morphological and

physiological attributes of each species. The growth and development of a seedling is in

stages. These stages are seed stage, seedling expansion stage, seedling seed- reserve stage,

seedling autonomous stage and juvenile stage (Garwood, 1996). The tropical tree species

exhibit high morphological diversity, but little is known about the functional significance of

this morphological diversity (Kitajima, 1996).




Initially the growth is primary and involves developments which terminate when direct

derivatives of apical meristems becomes mature. This growth produces roots, stem and leaves

in the seedling. Secondary growth which result from the activities of the vascular cambium,

occur in the latter stages and is responsible for the thickening of both roots and stem

(Kozlowski, 1971).




                                                 6
2.2.1 Growth of Milicia seedlings


Growth can be defined as the increase in mass due to division and enlargement of cells and

may be applied to an organism as a whole or any of its parts. All living organisms begin as a

single cell, which usually divides and keeps dividing until possibly billions of cells are

formed. As the various cells mature, they usually become larger and then differentiate. Thus,

they develop different forms adapted to specific functions such as conduction, support or

secretion of special substances (Stern, 1997). According to Levetin and McMahon (1999),

apical meristems are located at the tip of all roots and stems and contribute to the increase in

length of plants. Tissues that develop from these apical meristems are part of the primary

growth of the plant and give rise to the leaves and non-woody stems and roots. Some plants

have additional meristematic tissues that contribute to increases in diameter. These are the

vascular cambium and cork cambium. Tissues developing from these are considered part of

the plant secondary growth.




2.3    Factors Affecting Seedling Growth


Seedling growth and development revolve round carbohydrate manufacture and utilization.

Factors that influence the manufacture and utilization of carbohydrates and other biosynthetic

processes, affect the growth. These factors include water, light, temperature, herbivory and

other edaphic factors (Nwoboshie, 1982).




2.3.1 Water, Light and Temperature


Of all the factors controlling seedling growth, water is the most critical. Water is the vehicle

for all physiological and biochemical processes through which life is maintained.

                                               7
In the plant, opposing effect of transpiration and water absorption controls water. Whenever

transpiration is greater than absorption, the plant becomes dehydrated. A decrease in

hydration of protoplasm of cells in the meristematic tissues usually results in cessation or

checking of cell division or cell enlargement or both. If there are no limiting growth factors,

an increase in hydration of the protoplasm of a meristem usually results in an increase in the

rate of cell division and the cell enlargement phase of tree growth. However, all phases of

tree growth are not equally affected by the attenuation in the volume of water within the

seedling (Nwoboshie, 1982).




Light is the principal limiting factor for growth in all forests (Swaine et al, 1997). Light

affects growth through its effects on photosynthesis. It affects photosynthesis in terms of its

quality or wavelength composition, intensity or irradiance and duration. Light is important for

many physiological processes such as stomatal action permeability, absorption of electrolytes

as well as athocyanin and chlorophyll synthesis (Nwoboshie, 1982). Spatial variation in light

availability leads to variation in other physical and biotic environmental factors such as

temperatures, herbivore abundance and activities of pathogenic fungi and bacteria. Thus

successful seedling establishment in the under story or light gaps hinges upon species-

specific responses to these multiple factors confounded with light environment, not merely

upon light intensity, spectral quality or sun flecks (Kitajima, 1996).




Temperature affects plant growth through its effects on biochemical processes (Fitter and

Hay, 1987). Physiological and biochemical processes in plants are catalyzed by enzymes

which are active within certain temperatures range; hence plant can only growth within these

temperatures ranges. In the tropics, this rage is between 150C and 360C.

                                                8
Within the range, the growth of some plants increases with temperature while it is opposite

for other plants (Nwoboshie, 1982).




2.3.2 Herbivory


Herbivory is the consumption of plant biomass or parts of plants by animals. The parts

usually consumed are the fruits, seeds, leaves, twigs and buds. Mammals, birds and insect

defoliators are normally responsible for this. Seedlings are more prone to herbivory and this

may cause their early death or retard the growth of seedlings, though other factors may be

favourable.




The herbivores often prefer the young and fleshy leaves that may be rich in nutrients such as

nitrogen, phosphorus and potassium. According to Hall and Swaine (1986) plants have

defensive mechanisms to prevent being preyed upon. These mechanisms include hairs,

phytotoxins and thorns, shedding of damaged leaves and high leaf turn over in short-lived

leaves. Shade-tolerant seedlings appear to show greater defense and storage allocation than

the pioneer or shade intolerant seedlings (Kitajima, 1996).




2.3.3 Edaphic Factors


Although soil may vary considerably in structure and in physical, chemical and biotic

properties, the rate of growth of a seedling is influenced by those properties of the soil. From

the soil, the plant derives its nutrients and it is a storehouse for water and oxygen, all of

which are necessary for the physiological processes associated with growth.


                                               9
Hence the relative abundance of these factors in a particular soil, determine the rate at which

the seedling will grow on the soil (Brady, 1990).




2.4    Plant Fertilization


Fertilizer is any substance which is incorporated into the soil to increase crop growth and

yield by providing one or more of the elements essential for plant growth. Fertilizers are

applied to promote healthy growth, assist plants to overcome adverse effects of diseases or

insects or to correct mineral deficiencies, increase growth rate and maintain satisfactory vigor

(Evans, 1992).




Fertilizer can be applied anytime during the growing season if a seedling’s leaves turn

yellowish, experience extreme slow growth or some other signs. If fertilizers are to be applied

under hot, dry conditions, it is important to water the seedlings soon after the fertilizer

application so that the salt from the fertilizer does not damage the seedling root system

(Swanson, 2000). Plants need a number of essential elements to enable them to grow and

reproduce. These elemental nutrients may be classified as micronutrients and macronutrients.

The macronutrients (primary nutrients) include Nitrogen (N), Phosphorus (P) and Potassium

(K). Plants need these elements in relatively large quantities for their metabolism processes.

The most important of the macronutrients is Nitrogen (N) which is the most limiting nutrient

in the soil. It is generally known that nitrogen determines the yield of most crops more than

any other nutrient element provided there is adequate rainfall or water supply (Halley, 1982).




                                              10
The micronutrients Copper (Cu), Zinc (Zn), Manganese (Mn), Boron (B), Molybdenum

(Mo), Iron (Fe), Chlorine (Cl), Calcium (Ca), Magnesium (Mg) and Sulphur (S) are needed in

relatively small amounts and are generally found in sufficient quantities in normal pH

balanced soils. However, a deficiency in any of these nutrients can affect the health of

seedlings. The macronutrients have a role in building the structure of plants, whereas

micronutrients are important in enzyme systems and contribute to the plants function rather

than its structure (Halley, 1982; Brian and West, 1996).




2.5      Organic Fertilizer


Organic fertilizers are obtained from living sources, an example is manure. The most

noteworthy advantage of organic fertilizers is the fact that they are mostly insoluble and

therefore are slower to release nutrients to plants. This reduces the leaching effect that results

from most chemical fertilizers that causes so many problems (Zublena, 1996). Organic

fertilizers also help to improve soil quality. The consistent use of chemical fertilizers creates

plant life dependent upon synthetic fertilization as these fertilizers only work at the plant

level.




Through the introduction of organic matter and resulting improvement of the soil and

stimulation of the soil microbial activity, an environment can be created to support plant life

and provide a slow and consistent flow of nutrients to the plants. Organic fertilization is one

of the options for creating a long lasting and healthy plant-soil environment that is

ecologically responsible and economically viable for long term run (Hileman, 1972).




                                               11
2.5.1 Poultry Manure


Poultry manure is described as dropping from birds, which are kept domestically, especially

chickens. Chicken manure is the richest animal manure in terms of N, P and K (Russell,

1998). According to Hileman (1972), poultry manure is an excellent source of nutrients that

can be used in most fertilizer programs. The growth of the poultry industry in Ghana and the

corresponding increase in quantity and availability of poultry manure as well as its associated

environmental hazards has made it prudent to put poultry manure into an efficient use such as

raising seedlings in the nursery. Poultry manure has been found to be environmentally safe

source of fertilizer than inorganic fertilizer. Studies carried out to investigate the residual

effects of inorganic fertilizer on soil, destroyed soil organic and increased pests and disease

activities. The management of poultry manure can be a valuable source of nutrients for plants

and still ensure the safety of the environment (Brady, 1984).




2.5.2 Nutrient Value of Poultry Manure


Poultry manure is the most valuable of all manures produced by livestock. It has been used as

a source of plant nutrients and as a soil amendment. The type and amount of nutrients in

poultry manure and the nutrients’ eventual availability to plants may vary considerably

(Halley, 1982). Some factors affecting nutrient value of applied poultry manure include: type

of ration fed, method of collection and storage, amount of feed, bedding and/or water added,

time and method of application, soil characteristics, the crop to which manure is applied and

climate (Halley, 1982; Zublena et al., 1993). Hileman (1972) described poultry manure as

organic manure with high fertilizer value which is successfully used on wide variety of crops

as a valuable source of plant food. Increasing levels of various harmful elements (copper and

arsenic) and inorganic salts (sodium, calcium, potassium and magnesium) in feed will

                                              12
increase their concentrations in manure. There is concern about the potential toxic effects to

plants of high concentration of heavy metals and salts in soil, as a result of high application

rates of manure to the land. Generally, as the percent moisture of animal waste material

decreases, the percent nutrient content increases (Gale, 1997).


Table 2.1      the Percentage Composition of Poultry Manure


Manure         Organic matter         Ash            N              P 2 O5         K2O


Fresh manure            80            20             6.0            4.0            2.0
Dry matter)


Old manure              65            35             3.5            6.0            2.8
(Dry matter)

Source: Smith (1962).



About 30 percent of the total nitrogen in fresh manure is in the form of undigested food

residues; the remaining 70 percent is urinary nitrogen consisting of nearly 10 percent as

ammonium compounds and 60 percent as uric acid (Table 2.1). The faecal nitrogen is

relatively stable, but uric acid is a very high unstable compound in moist conditions and will

change into urea and ammonium salts even at fairly low temperatures. The loss of nitrogen is

only about 10 percent if fresh manure is dried quickly at a high temperature. It is best

therefore to spread manure directly on the field in wet weather; the rain facilitates the

incorporation of ammonia and soluble nitrogen compounds into the soil, where they are

absorbed and speedily converted into nitrates (Smith, 1962).




                                              13
2.5.3 Positive Effects of Poultry Manure


The effect of farmyard manure on humus is evident in the tropics. Agboola et al. (1975)

reported that a moderate application of manure on crop soils in the rainforest zone was

sufficient to slow down humus decomposition, which progress only half as fast as with

mineral fertilizers. The sorption power; that is the soil’s capacity to store and release

nutrients is also improved by manure application. Significant results have been obtained

when manure was applied to wetland rice (Müller-Sämann and Kotschi, 1994). Manure also

aids in reducing the incidence of some plant diseases. Mathur and Sinha (1966) studied the

influence of manuring on seedling-rot, root-rot and wilt of guar and found that the incidence

in all the cases was considerably reduced in manured soil. The reduction in disease incidence

was attributed to the increased plant vigour resulting from the high nutritive status of the

manured soil.




2.5.4 Potential Harmful Effects of Poultry Manure


In areas of intense poultry production, over fertilization of land with poultry manure occurs.

The result is suspected groundwater and surface water problems as excess nutrients run-off

the land or leach into groundwater supplies. Fresh stable manure is prone to form organic

acids. These are rapidly processed by soil organisms, which can lead to an overload of

oxygen and nitrogen in freshly manured soils (Gale, 1997). The C/N ratio of fresh manure is

often too high. This can result in a temporary N block such that hardly any nitrogen from

manure will be available in the following period. Manures are also costly per unit of plant

food (Halley, 1982; Müller-Sämann and Kotschi, 1994).




                                             14
CHAPTER THREE


                           RESEARCH METHODOLOGY


3.1    Study Area

The experiment was conducted at the Faculty of Renewable Natural Resources

Demonstration Farm (KNUST-Kumasi). This area falls within Moist Semi-deciduous

Vegetation Zone of West Africa. The area is characterized by a bimodal rainfall pattern with

the major wet season between May and July. This area experiences a short dry season in

August and a long one between December and March. The annual rainfall of the area ranges

between 1250 mm -1500 mm. The soil in the study site belongs to the family Ferric Acrisols

in the soil taxonomy. Ferric Acrisols are loamy sand, well drained but strongly acidic (Adu

and Asiamah, 1992).




3.2    Research Design

The experimental design used in this field experiment was a Randomized Complete Block

Design. The randomized complete block design is one of the most widely used experimental

designs in natural resources research. Blocking is done to reduce experimental error by

eliminating the contribution of known sources of variation among experimental units (Nkyi,

2009). Two-month old Milicia excelsa seedlings were obtained from the Forestry Research

Institute of Ghana (FORIG), Kumasi-Ghana. The poultry manure was obtained from the

Animal Science Department of the Faculty of Agriculture (KNUST-Ayeduase). Other tools

and equipment used included cutlass, rake, watering can, tape measure, hand fork and hoe for

the preparation of the planting bed.




                                            15
The plant parameters measured were the height (cm), stem diameter (mm) and the number of

leaves. According to Mohr and Schopfer (1995), height and stem diameter are some of the

frequently used methods of measuring the growth of multi-cellular living systems and often

advantageous to use several characteristics for the same system.




Leaves are also an important part of plants; they help in the process of photosynthesis. Leaves

have their own definite shape and arrangement according to requirements of the plant. Leaves

trap energy from sunlight and convert it into pure compounds. Leaves were counted visually.

An electronic caliper was used in measuring the stem diameter while the height was

measured with a meter rule. Data on the height, stem diameter and number of leaves were

collected two days after transplanting and then fortnightly over the twelve weeks of the

research. The experiment was conducted from 23rd November, 2010 to 19th February, 2011.




3.2.1 Experimental Design and Layout

The experimental design used was a Randomized Complete Block Design. The study was

carried out in three blocks, each block consisting of five plots (Figure 3.1). The poultry

manure was applied at the rate of 17,500 kg/ha as recommended by Zublena et al., (1993).

Five levels of the poultry manure were used for the experiment. T1 (0.0 Kg), T2 (0.90 Kg),

T3 (1.80 Kg), T4 (2.70 Kg) and T5 (3.60 Kg)




                                              16
BLOCK 1                         BLOCK 2                        BLOCK 3


           Plot 1=T2                        Plot 1=T2                      Plot 1=T3


           Plot 2=T4                        Plot 2=T5                      Plot 2=T2
7.0 m




           Plot 3=T1                        Plot 3=T4                      Plot 3=T5


           Plot 4=T5                        Plot 4=T1                      Plot 4=T4


           Plot 5=T3                        Plot 5=T3                      Plot 5=T1

            1.0 m              0.5 m         1.0 m          0.5 m           1.0 m


  Figure 3.1 RCBD Experimental layouts with the allocated treatment.




  3.2.2       Experimental Procedures


  Three beds representing the blocks of size 1.0 m × 5.0 m (5.0 m2) each and plots with

  dimensions of 1.0 m × 1.0 m (1.0 m2) were constructed with spacing of 50 cm between the

  blocks and plots making the total plot length of 7.0 m with an area of 7.0 m 2. The various

  treatments were randomly allocated to the plots (Fig 3.1) with eight seedlings per plot.

  Reference points of 1cm above the soil surface of the seedlings were marked with non-

  poisonous indelible ink to provide consistency at the point of the height and diameter

  measurement. The total number of experimental plots was fifteen. The poultry manure was

  applied at the rate of 17,500 Kg/ha as recommended by Zublena et al., (1993). Rates of

  poultry manure application were therefore applied based on the following calculation;

  10000 m2 (1 hectare) = 17500 Kg.


                         1.0 m 2 X17500 Kg
  1.0 m2 (plot size) =                     = 1.75 Kg/plot ≈ 1.80 kg/plot (average application).
                             10000 m 2

                                                  17
The recommended rate per plot was halved, doubled and multiplied by one-half to achieve

the various treatment levels. Five levels of the poultry manure were used for the experiment.

T1 (0.0 Kg, control), T2 (0.90 Kg, halved), T3 (1.80 Kg, recommended rate per plot), T4

(2.70 Kg, multiplied by one-half) and T5 (3.60 Kg, doubled). The poultry manure was

applied to the soil two weeks before transplanting the seedlings to the experimental plots to

allow the ammonia to be nitrified so that it will not burn the young plants as recommended by

Smith (1962).




 3.3   Cultural Practices on the Experimental Plots


 Seedlings were transplanted from the poly bags when they were two months old. The

 transplanting exercise was undertaken late in the afternoon after the bed had been watered

 thoroughly. According to Hilary (2009), the best time of day to plant is in the late afternoon

 when the sun is not so hot.




 By taking advantage of this time of day, the new plants are able to acclimatize overnight.

 Strong sun and wind have a potentially adverse effect on new transplants and unless watered

 carefully, and in some cases sheltered from the wind and sun, they can severely wilt. This

 places the plants under stress at the very beginning of their growing cycle. This is not a good

 idea because sometimes they never bounce back and do not thrive as well as they could

 have. Watering of the transplanted seedlings was done immediately after transplanting and

 twice daily and evenly with each plot receiving about the same volume of water. Plots were

 not watered after heavy rains due to high incidence of fungal infestation when the plant

 roots are overwatered (Swanson, 2000).



                                              18
Weeds that appeared on the beds were controlled by hand-picking to prevent competition for

water, nutrients, space and light. Weeds that appeared between the beds were hoed to

eliminate any type of competition. According to Townsend and Sinden (1999), weeds host

pests and diseases that can spread to cultivated crops. Weeds also impose costs on producers

in two ways; through reductions in the quality and quantity of yields, and increases in input

requirements for weed control. This cost may have economic consequences for the wider

community if a large number of farmers are affected, leading to variations in supplies and

prices of commodities.



3.4.   Data collection

An indelible ink was used to mark each seedling 1cm above the soil, where the diameter and

height readings were taken so that irregularity of the soil around the seedlings would not

affect the recording. Initial measurements of both the heights and the diameters were taken

two days and two weeks after transplanting and application of the treatments respectively.

Subsequent readings were taken every two weeks for a period of three months within which

seven readings were recorded.




3.5    Data Processing and Analysis


All data collected were subjected to a one-way Analysis of Variance (ANOVA). Microsoft

excel was used to compute the increment of the various plant parameters measured. Least

Significant Difference (LSD) was used to separate treatment means that differed

significantly. Any treatment mean with a difference more than the calculated Least

Significant Difference was interpreted as significant and ascribed ** and those without any
                                   ns
significant difference were ascribed .


                                             19
This was done for all the plant growth parameters measured with the exception of the

survival percentage. Coefficient of Variation was used to ascertain the acceptance of the

experiment as recommended by Nkyi (2009) that the Coefficient of Variation should not be

greater than 20 percent, otherwise the number of blocks should be increased or the

experiment rejected.




                                                           (Observed value - Expected value) 2
The Chi-Square (X2) method with the formula: X2 =      {                                       }
                                                                    Expected value

was used to determine the significance of the poultry manure on the seedling percentage of

survival at a significant level of 5%. A Chi- Square value higher than the calculated value

renders the effect insignificant and vice versa. The results are represented using appropriate

graphs and tables.




                                             20
CHAPTER FOUR


                                         RESULTS


4.1    Height measurements of Milicia excelsa seedlings


Almost all the treatments T1 (0.0 Kg) T2 (0.90 Kg), T3 (1.80 Kg), T4 (2.70 Kg) and T5

(3.60 Kg) showed increment in height throughout the experimental period. However,

Treatment (T1) and Treatment T5 showed a decrease in height in the eighth week with

Treatment T1 recording the minimum increment in height and Treatment T4, the highest

increment in height, (Fig.4.1). The experiment showed that, from the 2nd to the 6th week

there were low increments in height for all the treatments. Treatment T1 and Treatment T5

had the same increment within the first four weeks. However Treatment T1 had a decrease in

height between the 6th and 8th week. From the 10th to the 12th weeks, Treatment T4

recorded the highest mean height increment (Fig 4.1).




The Analysis of Variance (ANOVA) carried out indicated that the treatments were

significantly different at 5% level of significant on mean height increment of the seedlings

(F0.05, 4, 8= 8.40 ≥ F0=3.84). Least Significant Difference (LSD) analysis revealed that, there

were significant differences between T1 (0kg) and each of T2, T3, T4 and T5 but no

significant difference among T2 and T3, T5 as well as between T3 and (T4 and T5). It was

observed that there is a drastic decrease in the height increment between week 6 and week 8

The initial mean height increment for all the treatment levels recorded after fertilization were;

T1= 9.17 cm, T2= 9.88 cm, T3= 10.13 cm T4= 9.70 cm, T5= 10.00 cm as against 19.25 cm,

23.72 cm, 25.19 cm, 30.28 cm and 24.00 cm for treatments T1, T2, T3, T4, and T5,




                                               21
respectively as the values recorded at the time the experiment was terminated on 19th

February, 2011.


                              9
                              8
      Height increment (cm)




                              7                                                            T1

                              6
                                                                                           T2
                              5
                              4                                                            T3

                              3
                                                                                           T4
                              2
                              1                                                            T5
                              0
                                        Week 2 Week 4 Week 6       Week8 Week 10 Week 12
                                               Weeks after transplanting



Fig 4.1 Mean Height increments of Milicia excelsa seedlings.



4.2                           Diameter measurements of Milicia excelsa seedlings


Diameter increments were observed for all the treatments throughout the experiment period,

(Fig 4.2). For the first six weeks after the application of the treatments, the increments were

high for all treatments except treatment T5 which had a low increment of 8.69 cm. The

increments for all the treatments decreased from the 8th to the 10th week. There were steady

increments for treatments T1, T3 and T4 between week 10 and week 12 while treatments T2

and T5 were not significantly different. Treatment T4 had the highest mean increment

followed by T3 and T2 with treatment T1 recording the least mean diameter increment.


The results of the Analysis of Variance (ANOVA) showed that, all the treatments had no

significant effect on the diameter increments of the seedlings at a significant level of 5%


                                                              22
(F0.05,4,8 = 3.74 ≤ F0 = 3.84). Least Significant Difference (LSD) showed that, there were

significant differences between T1 (0.0 Kg) and T4 (2.70 Kg), and treatments T4 and T5 (3.6

Kg) but no significant difference among T1 and each of T2 (0.9 Kg), T3 (1.80 Kg), and T5.

Again, there were no significant difference among T2, T3 and T4.


                                1.2
      Diameter increment (mm)




                                 1                                                             T1

                                0.8                                                            T2

                                0.6                                                            T3

                                0.4                                                            T4

                                0.2                                                            T5

                                 0
                                            Week 2   Week 4   Week 6   Week8 Week 10 Week 12
                                                     Weeks after transplanting


Fig.4.2 Mean diameter increments of Milicia excelsa seedlings.




4.3                             Mean Number of Leaves of Milicia excelsa seedlings

All the treatments showed increment in mean number of leaves throughout the experimental

period. However, Treatment T1 (0.0 Kg) showed the lowest increment and Treatment T4

recorded the highest increment, (Fig.4.3). The experiment showed that, from the 2nd to the

6th week low increments were recorded for all the treatments, (Fig 4.3). Between the 6th and

10th week, there were steady increments of the mean number of leaves for Treatments T2

(0.9 Kg), T3 (1.80 Kg), T4 (2.70 Kg and T5 (3.60 Kg) while Treatment T1 still remained

almost the same as the first six weeks.



                                                                 23
From the 10th to the 12th week, the mean number of leaves remained the same for all the

treatments except treatment T4. Analysis of Variance (ANOVA) at 5% significance level

showed that poultry manure had a significant effect on mean number of leaves (F0.05,              4, 8=


48.81 ≥ F0=3.84). Least Significant Difference (LSD) showed that, there were significant

differences between almost all the treatment means but no significant difference among T1

and each of T2, and T3 as well as between treatment T3 and treatment T4. The mean number

of leaves at the end of the study period were T1=7.67, T2=7.67, T3=10.00, T4=19.67 and

T5=14.0


                              18

                              16
                                                                                             T1
                              14
      Mean Number of Leaves




                              12                                                             T2

                              10
                                                                                             T3
                               8

                               6                                                             T4

                               4
                                                                                             T5
                               2

                               0
                                    Week 2   Week 4   Week 6    Week 8   Week 10   Week 12
                                                  Weeks After Transplanting


Fig.4.3 Mean Number of Leaves of Milicia excelsa seedlings.



4.4                           Percentage Survival of Milicia excelsa seedlings

Three months after transplanting, the percentage survival of the Milicia excelsa seedlings

ranged from 87.50% to 100% (Fig4.4). There were significant differences in the rate of

survival between the various treatments with a survival expectancy of 60% (x²=30.74 >


                                                               24
23.70, p=0.05). All the treatments recorded no mortality during the first six weeks after

transplanting. However, treatment T1 recorded three plants mortality representing 12.50

percentage of mortality in the eighth week. All other treatments recorded mortality as low as

zero percent. The total mortality over the entire study occurred in the first eight weeks. There

was no mortality after 8 weeks of the experimental period and all the treatments (T2, T3, T4,

and T5) except treatment T1 had the same percentage survival of 100 percent throughout the

study period.


                         102
                         100
                          98
   Percentage Survival




                          96
                          94
                          92
                          90
                          88
                          86
                          84
                          82
                          80
                               T1   T2             T3             T4              T5
                                         Treatments



Fig.4.4 Percentage survival of Milicia excelsa seedlings




                                              25
CHAPTER FIVE


                                       DISCUSSION


5.1      Height increments of Milicia excelsa seedlings


All the treatments increased in height throughout the study period, Fig 4.1. Analysis of

Variance (ANOVA) tested at 5% significance level showed a significant effect of poultry

manure on the mean height increments. However, the degree of increment varied among the

treatments. There was low height increments recorded for all the treatments between the 2nd

and 6th weeks and even a decrease in seedling height increment for the 8th week. This might

be due to the fact that the poultry manure applied had not yet fully decomposed to reach the

roots of the seedlings for it to be absorbed. Therefore the little fertility in the soil was then

used by the seedlings. The significant increase in the height of the Milicia excelsa seedlings

might be due to the nutrient contribution from decomposing poultry manure. The effect of T4

(2.7 Kg of manure) was greater than that of T1 (0 Kg of manure). This revealed a sharper

growth with increasing rate of manure application. This confirms the assertion by Duryea and

Brow (1984) that seedlings grown at fairly higher fertilization levels produced higher growth

rates.




From the 8th to the 10th week, there were steady and sharp increases in heights for T1, T4 and

T5; however, T2 and T3 almost had a constant stem increment. Smith, (1962) reported that

poultry manure may be of little immediate value in correcting nutrient deficiencies since it

takes time for it to decompose and release nutrients to plants roots. The role played by the

three primary nutrients (N P K) is vital in the process of plant development.



                                               26
The significant increase in the height of the seedlings might be due to the nutrient

contribution from decomposing poultry manure.




The application of 2.7 Kg of manure T4, performed better than when 0.9 Kg of manure T2

was applied. The performance of T4 (2.7 Kg of manure) could be attributed to the increased

supply of nitrogen (N). This might have increased the meristematic and development

activities through the differentiation of tissues and have therefore increased growth with

respect to the height of the seedlings. This result confirms the findings of Mohan and Sharma

(1992) who worked on the effect of nitrogen and sulphur on the growth and yield of mustard

seedlings.




Hileman (1972) described poultry manure as organic manure with high fertilizer value which

is successfully used on a variety of crops. Zublena et al. (1993) also noted that the organic

matter in soil improves moisture and nutrient retention. These properties of high fertilizer

value, improvement in moisture and nutrient retention helped in increasing the rate of growth

and subsequently produced viable and healthy seedlings that can withstand adverse weather

conditions. Therefore the presence of these nutrients in sufficient amounts resulted in

vigorous growth of the seedlings. From the 10th to 14th week, the mean height increments

continued to increase for all the treatments except for T1. Organic fertilizers are one of the

options for creating a long lasting and healthy plant-soil environment that is ecologically

responsible and economically viable for long term supply of nutrients for plant growth and

development (Gale, 1997).




                                             27
The research alternate hypothesis for this research that different levels of poultry manure

would provide environmental conditions favourable for the growth, development Milicia

excelsa seedlings is therefore accepted and the null hypothesis rejected.




5.2    Diameter increments of Milicia excelsa seedlings


All the treatments (T1, T2, T3, T4 and T5) had no increasing effect on the seedling stem

diameter throughout the study period according to the Analysis of Variance (ANOVA) tested

at 5% significance level of the Milicia excelsa seedlings. Also, the degree of increment varied

among the treatments with T1 being the least and T4 as the highest. Low increments in

diameter were recorded for all the treatments between the 2nd and 6th week. This might be due

to the fact that the poultry manure applied was being used for apical meristematic growth.

Initially the growth is primary and involves developments which terminate when direct

derivatives of apical meristems becomes mature. This growth produces roots, stem and leaves

in the seedling. Secondary growth which result from the activities of the vascular cambium,

occur in the latter stages and is responsible for the thickening of both roots and stem diameter

(Kozlowski, 1971).




5.3    Mean Number of Leaves of Milicia excelsa seedlings


All the treatments showed increment in mean number of leaves throughout the experiment

period. However, Treatment one T1 showed the minimum increment and Treatment T4

recorded the highest increment, (Fig.4.3). Analysis of Variance (ANOVA) at 5% significance

level showed a significant effect of poultry manure on the mean number of leaves.




                                              28
This significant increment might be due to the availability of nutrients for plant growth

especially in the leaf tissues. This confirms the assertion by Kozlowski (1971) that the initial

growth of seedlings is primary and involves developments which terminate when direct

derivatives of apical meristems becomes mature.




This growth produces roots, stem and leaves in the seedling. Secondary growth which result

from the activities of the vascular cambium, occur in the latter stages and is responsible for

the thickening of both roots and stem diameter. The alternate hypothesis for this research that

different levels of poultry manure would provide environmental conditions favourable for the

growth, development Milicia excelsa seedlings is again accepted and the null hypothesis

rejected.




5.4    Percentage Survival of Milicia excelsa seedlings.


Three months after transplanting, the percentage survival of the Milicia excelsa seedlings

ranged from 87.5 to 100 percent (Fig4.4). According to a Chi-Square (x2) test carried out it

revealed that, there was a significant effect of the poultry manure applied to the seedlings

with a survival expectancy of 60 percent at significant level of 5%. All the treatments (T1,

T2, T3, T4 and T5) recorded no mortality during the first six weeks after transplanting.

However, three mortalities of plants were recorded during the first 8 weeks representing

about 12.50% of mortality in the eighth week for treatment T1.




All other treatments recorded mortality of 0%. The total mortality over the entire study

occurred in the first eight (8) weeks with only one plant dead. This might be due to low

                                              29
supply of water to the seedling growth and development during the dry season of the

research. Nwoboshie, (1982) reported that of all the factors controlling seedling growth,

water is the most critical. Water is the vehicle for all physiological and biochemical process

through which life is maintained. Whenever transpiration is greater than absorption, the plant

becomes dehydrated. A decrease in hydration of protoplasm of cells in the meristematic

tissues usually results in cessation or checking of cell division or cell enlargement or both. No

mortality was encountered after the first 8 weeks throughout the three months of the study

period.




The percentage of the seedling survival may be as a result of the improved level of the soil

nutrient for the plant growth, development and survival. The alternate hypothesis for this

research that different levels of poultry manure would provide environmental conditions

favourable for the growth, development and survival Milicia excelsa seedlings is accepted

and the null hypothesis rejected.




                                               30
CHAPTER SIX


                 CONCLUSIONS AND RECOMMENDATIONS


6.1    Conclusions

6.1.1 Effect of poultry manure on vegetative growth of Milicia excelsa

seedlings


The study indicates that poultry manure is a valuable fertilizer because application of the

poultry manure resulted in a significant effect on the mean stem height of Milicia excelsa

seedlings. However, there was no significant effect on the species diameter.




6.1.2 Effect of poultry manure on the percentage survival of Milicia excelsa

seedlings


Again the poultry manure had a significant effect on the percentage survival of the Milicia

excelsa seedlings. An application rate of 27000 Kg/ha was capable of enhancing the survival

of the Milicia excelsa seedlings by 87.50 percent over the control.




6.1.3 Effect of poultry manure on the mean number of leaves of Milicia

excelsa seedlings


Poultry manure also had a significant effect on the mean number of leaves and can therefore

be applied to Milicia excelsa seedlings for raising healthy and good seedlings in the nursery

as well as for its plantation establishment.




                                               31
In general, the introduction of Milicia excelsa into plantations by enhancing its early growth

performance could have beneficial effects on the forest of Ghana, since it will reduce the high

dependency on the forest for Milicia excelsa species for subsistence or commercial purposes.




6.2    Recommendations

Since the poultry manure significantly increased the growth of the Milicia excelsa seedlings,

their application should be encouraged for the production of strong and healthy seedlings for

plantation purposes with a recommended rate of 27,000Kg/ha. This will serve as a substitute

for inorganic fertilizers thereby reducing cost of inputs for the farmer.




It may be worthwhile considering the application of poultry manure in the early stages of

seedling nursing so as to reduce plant shock during transplanting. Further research should be

carried on the seedlings for a long period of time of about thirteen to fifteen months, so as to

ascertain the findings obtained from this research work.




                                               32
REFERENCES

Adu, S.V. and Asiama, R.D. 1992. Soils of Ayensu-Densu Basin, Ghana. Soil Research
       Institute of Ghana: 34pp.


Brooks, R.L. 1949. Gold Coast Timber. The Government Printing Department, Takoradi
       Branch, Gold Coast, 39pp.


Duryea, M.L. and Brow, G.N. 1984. Seedling physiology and reforestation success. Matrinus
       Nijhoff/Dr. W. Junk Puplishers: 232 pp.


Evans, J., 1992. Plantation Forestry in the Tropics, 2nd Ed. Calderon Press Oxford, New
       York. USA.


FAO, 1986. Some medicinal plants of Africa and Latin America. FAO Forestry paper 67.
       FAO of Rome. Pp69-74.


Fitter, A.H and R.K.M Hay. 1987. Environmental physiology of plants. 2nd Edition,
       Academic Press Ltd. 423pp.


Gale, A. B. 1997. Application of poultry manure. Updated 25th February, 1997.
        http://www.bae.uga.edu/extension/pubs/c826-ed.html. Accessed 8th September,
        2010.


Garwood, N.C. 1996. Functional morphology of tropical seedlings. Pp 55-188. In: M.D
       swaine, ed. Ecology of tropical tree seedlings. UNESCO.


Hall, J.B and M.D. Swaine. 1981. Distribution and ecology of vascular plants in tropical rain
       forest vegetation in Ghana. Dr. W. Junk Publishers, the Hague- Boston-London.
       Pp383.


Halley, R.J. 1982. The Agricultural Notebook. 17th edition. Butterworths and Co.
       (Publishers).


                                             33
Hawthorne, W. 1990. Field guide to the forest trees of Ghana. Chatham: Natural Resources
       Institute for oversees development Administration, London. Ghana Forestry Series 1,
       VI +278pp.


Hileman, L.H. 1972. Transactional dynamics of poultry manure in soil. Paper presented at
       1972 Winter Meeting American Society of Agricultural Engineers, St. Joseph,
       Michigan: 15pp


Irvine, F.R. 1961. Woody plants of Ghana. Oxford University Press. London. 868pp.


Jones N. and J.H. Miller. 1992. Jatropha carcass a multipurpose tree species for problematic

       sites. The World Bank, Washington, D.C. U.S.A.




Kitajima, K. 1996. Ecophysiology of tropical seedlings.. In: S.S Mulkey, R.L Chazdon and
       A.P. Smith, eds. Tropical forest plants ecophysiology. Chapman and Hall. Pp 559-596




Kotey, E.N.A., Francois, J., Owusu, J.G.K., Yeboah R., Amanor, K.S. and Antwi, L. 1998.
       Falling into place: Policy that works for forests and people. Series no. 4. International
       Institute for Environment and Development. London.




Kozlowski, T.T. 1971. Growth and development of trees. Vol. 1. Academic Press, N.Y.
       London. Ltd. London, Boston



Levetin E. and McMahon K. 1999. Plant and Society. 2nd edition, McGraw-Hill Inc.
       University of Tulsa, New York, USA, pp 32.


MOFA. 1998. National Soil Fertility Management. Action Plan. Accra, Ghana.




                                              34
Mohan, K., and Sharma H.C. 1992. Effect of nitrogen and sulphur on growth, yield
       attributes of seed and oil of mustard (Brassica juncea). Indian Journal of Agronomy
       37 (4): 748-54.


Mohr H. and Schopfer P. 1995. Plant physiology, Springer-Verlag, Berlin Heidelberg, Hong
       Kong. Pp 294.


Müller-Sämann, K. and Kotschi, J. 1994. Sustaining Growth: Soil fertility management in

       New York.


Nicholas, J.D., F.B. Agurgo, V. K. Agyeman, M.R. Wagner and J.R. Cobbinah. 1998.
       (Distribution and abundance of Milicia excelsa in Ghana). Ghana Journal of Forestry,
       vol.6 1998. Pp 1-7.




Nkyi-Appiagyei, K. 2009. Practical Experimental Design and analysis in Natural Resources
       Management, King Bernard Printing Press, Kumasi- Ghana. Pp 36-52.




Nwoboshie, L.C. 1982. Tropical silviculture: principles and techniques. Ibadan University
       Press. 333pp.




Oteng-Amoako, A.A., 2006. Tropical African Timber Trees from Ghana, G-Pak press,

       Accra-Ghana.




Russell, E.W 1998. Soil condition and plant growth. 11th edition, Longman Publication, UK.
       Pp 34




Smith A.M., 1962.Manures and fertilizer, Thomas and sons Ltd. Canada. 70-72p.



                                            35
Stern, K.R. 1997. Introductory plant biology. 7th edition, McGraw- Hill Inc. California State
       University, Chico. Pp 181.




Swaine, M.D., V.K. Agyeman, B. Kyere, T.K. Orgle, J. Thompson and E.M Veeneendal.
       1997. Ecology of forest trees of Ghana. OAD Forestry Series No. 7 University of
       Aberdeen. 76pp.




Swanson, B. 2000. Tree fertilization: A guide for fertilizing New and Established Trees in
       Landscape. Clarendon Press, Oxford UK, Pp 221.




Taylor, C.J. 1960. Synecology and silviculture in Ghana. Nelson and sons Ltd. Edinburg,
       418pp




Townsend J. and J. A. Sinden, 1999. Economic impacts of noxious weeds, other weeds, and
       tree growth, on agricultural production, University of New England, England UK,
       Pp. 4



White,T.C.R. 1966. Food and outbreaks of phytophagous insects. Ph. D Thesis, Adelaide
       University, Australia.




Young, A. 1976. Tropical soils and soil survey. Cambridge, Cambridge University Press:
       467pp


Zublena, J.P., Barker, J.C. and Carter, T.A. 1993. Poultry manure as a fertilizer source.
       North Carolina Cooperation Extension Service. Soil Facts. Rayleigh, N.C.




                                             36
APPENDICES


APPENDIX 1           Analysis of Variance (ANOVA) for Poultry Manure on the Mean
Stem Height of Milicia excelsa seedlings

Sources of Variation Sum of squares Degree of Freedom Mean sum of squares F0                   F-critical

Treatment                 216.78                  4                 54.20              8.40** 3.84
                                                                                              ns
Blocks                    53.80                   2                 26.90              4.17        4.46

Residual                  51.61                   8                 6.45

Total                     322.19                  14
                                   ns
**Significant at α = 5%                 Not significant at α = 5%           C.V = 10.00%



APPENDIX 2           Least Significant Difference (LSD) for Mean Stem Height at 5%
Significance level



Least Significant Difference        Treatment Means             Differences in Treatment Mean

4.790                                      y₁=19.25             y₁ - y₂=19.25-24.05= 4.80*

                                           y₂=24.05                 y₁ - y₃=19.25-27.53= 8.28*

                                           y₃=27.53                 y₁ - y₄=19.25-30.70= 11.45*

                                           y₄=30.70                 y₁ - y₅=19.45-25.45= 6.20*
                                                                                              ns
                                           y₅=25.45                 y₂ - y₃=24.05-27.53=3.48

                                                                    y₂ - y₄=24.05-30.70= 6.65*

                                                                    y₂ - y₅=24.05-25.45= 1.40ns

                                                                    y₃ - y₄=27.53-30.70= 3.17ns

                                                                    y₃ - y₅=27.53-25.45= 2.08ns

                                                                    y₄ - y₅=30.70-25.45= 5.25*

      * = Significant at 5% Significance level.                    y₁=T1, y₂=T2, y₃=T3, y₄=T4, y₅=T5

      ns= Not significant at 5% Significance level.



                                                   37
APPENDIX 3         Analysis of Variance (ANOVA) for Poultry Manure on the Mean
Number of Leaves of Milicia excelsa Seedlings.

Sources of Variation Sum of squares Degree of Freedom Mean sum of squares F0                  F- critical

Treatment                   312.4                  4                 78.10          48.81 * 3.84

Blocks                     1.20                    2                 0.60           0.38ns        4.46

Residual                   12.80                   8                 1.60

Total                       326.40                 14
                                    ns
**Significant at α = 1%                  Not significant at α = 5%           C.V = 10.68%



APPENDIX 4           Least Significant Difference (LSD) for Mean Number of Leaves at 5%
Significance level



Least Significant Difference         Treatment Means             Differences in Treatment Mean

2.390                                       y₁=7.67             y₁ - y₂=7.67-7.67=0.00ns

                                            y₂=7.67             y₁ - y₃=7.67-10.00= 2.33ns

                                            y₃=10.00            y₁ - y₄=7.67-19.67= 12.00*

                                            y₄=19.67            y₁ - y₅=7.76-14.00= 6.33*

                                            y₅=14.00            y₂ - y₃= 7.67-10.00= 2.33ns

                                                                y₂ - y₄=7.67-19.67= 12.00*

                                                                y₂ - y₅=7.67-14.00=6.33*

                                                                y₃ - y₄=10.00-19.67= 9.67*

                                                                y₃ - y₅=10.00-14.00= 4.00*

                                                                y₄ - y₅=19.67-14.00= 5.67*

      * = Significant at 5% Significance level.                 y₁=T1, y₂=T2, y₃=T3, y₄=T4, y₅=T5

      ns= not significant at 5% Significance level.




                                                      38
APPENDIX 5         Analysis of Variance (ANOVA) for Poultry Manure on the Mean
Stem Diameter of Milicia excelsa Seedlings



Source of Variation Sum of Squares Degrees of Freedom Mean Sum of Squares F0                F- critical
                                                                                           ns
Treatment            2.66                4                    0.665                  3.74       3.84

Blocks                4.21               2                    2.107                  11.84** 4.46

Residual              1.42                8                   0.178

Total                8.30                 14
                                  ns
**Significant at α = 1%                Not significant at α = 5%           C.V = 10.58%



APPENDIX 6           Least Significant Difference (LSD) for Mean Stem Diameter at 5%
Significance level



Least Significant Difference       Treatment Means             Differences in Treatment Mean

0.796                                     y₁=3.66              y₁ - y₂=3.66-4.05= 0.39ns

                                          y₂=4.05              y₁ - y₃=3.66-4.14= 0.48ns

                                          y₃=4.14              y₁ - y₄=3.66-4.68= 1.02*

                                          y₄=4.68              y₁ - y₅=3.66-3.46= 0.20ns
                                                                                       ns
                                          y₅=3.46              y₂ - y₃=4.04-4.14= 0.09

                                                               y₂ - y₄=4.04-4.68=0.63ns

                                                               y₂ - y₅=4.04-3.46=0.59ns

                                                               y₃ - y₄=4.14-4.68= 0.54ns

                                                               y₃ - y₅=4.14-3.46=0.68ns

                                                               y₄ - y₅=4.68-3.46=1.22*

      * = Significant at 5% Significance level.                   y₁=T1, y₂=T2, y₃=T3, y₄=T4, y₅=T5

      ns = not significant at 5% Significance level.




                                                    39

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B sc. research work

  • 1. CHAPTER ONE INTRODUCTION 1.1 Background to the study The growth of plants depends on the availability of nutrients from the soil. Thus, it is important that the soil should potentially provide nutrients for the growth and development of plants. Prolonged uptake of nutrients by growing plants depletes soil of vital nutrients, adversely affecting the growth of plants. Organic manure can be added in order to compensate for the losses due to leaching and uptake by existing plants from the soil (Russell, 1998). Milicia excelsa formerly called Chlorophora excelsa belongs to the family Moraceae. The tree is mostly found in West, Central and East Africa, extending from Guinea Bissau to Mozambique. Milicia excelsa is a durable wood used for the purposes of exterior and interior joinery, frames and doors, luxury cabinet works and garden furniture. Other uses include floorings, steps and stairs, paneling and moldings, decorative veneer, plywood and the construction of vehicle and truck bodies (Oteng-Amoako, 2006). The high demand for the wood and its other products has resulted in over exploitation. The species is now considered as a scarlet species; these are species that are common but under more imminent threat. Currently it has over 200 % exploitation rate by the Forestry Department of Ghana and requires special permit for it to be harvested (The Ghana Forest Service, 1998). To replenish the stocking of such valuable species, its plantations were established. Seedlings of Milicia excelsa raised for plantation purposes appear weak and slender in form and hardly withstand the adverse conditions of the weather making it very 1
  • 2. difficult in raising healthy seedlings and this affects the species growth performance as well as its survival rate in the establishment of its plantation (Irvine, 1961). Addition of poultry manure to improve the nutrient status of the growth medium (soil) can enhance the general growth performance of seedlings in a nursery. The introduction of Milicia excelsa into plantations could have beneficial effects on the forest of Ghana, since it will reduce the high dependency on the forest for Milicia excelsa species for subsistence or commercial purposes. However, for a plantation program to yield maximum environmental and economic benefits, healthy and good seedlings should be supplied inexpensively (Appiah, 1998). 1.2 The Problem statement Seedlings of Milicia excelsa raised for plantation purposes appear weak and slender in form and hardly withstand the adverse conditions of the weather making it very difficult in raising healthy seedlings and this affects the species growth performance as well as its survival rate in the establishment of its plantation (Irvine, 1961). There is therefore the need to investigate possible solutions to this problem in order to enhance the species growth performance. 1.3 Justification of the study Manuring can help increase the nutrient status of soils depleted due to leaching and uptake by existing plants from the soil. A lot of effort has been put into the promotion of the use of mineral fertilizers for crop production, not much seems to have been done in the use of organic forms of fertilization for soil fertility amelioration (MOFA, 1998). 2
  • 3. The use of organic manure preferably, poultry manure will help and encourage the establishments of Milicia excelsa plantations. This will facilitate increasing supply of Milicia excelsa timber products in the world market. 1.4 Aim and objectives This study aims at determining the effect of organic manure on the early growth performance and the percentage survival of Milicia excelsa seedlings. Specific objectives 1. To determine the effect of poultry manure on the vegetative growth (stem height and diameter) of Milicia excelsa seedlings. 2. To determine the effect of poultry manure on the percentage survival of Milicia excelsa seedlings. 3. To determine the effect of poultry manure on the mean number of Milicia excelsa seedling leaves over some period of time. 1.5 The research hypothesis The research null hypothesis was that poultry manure would not provide environmental conditions favourable for the growth and development of Milicia excelsa seedlings. However, the alternate hypothesis for this research was that different levels of poultry manure would provide environmental conditions favourable for the growth, development and survival of Milicia excelsa seedlings. 3
  • 4. CHAPTER TWO LITERATURE REVIEW 2.1 The Milicia Species Milicia excelsa formerly known as Chlorophora excelsa and locally known as “Odum” belongs to the family Moraceae. In Africa the genus Milicia, has two species, M. excelsa and M. regia. The African species are very similar and are not distinguished in the timber trade, but are commonly referred to as “Iroko” (Hawthorne, 1990). Milicia excelsa is currently found in forests of Africa stretching across the West Africa sub- region from Senegal through Cote D’ Ivoire, Ghana to Nigeria. Other places of occurrence include Angola, Mozambique and Tanzania (Hall and Swaine, 1981). Guinko (1985) cited by Cobbinah (1992) speculated that the presence of M. excelsa in fetish worship sites or on sites of former special cemeteries is an indication that the species may have a wide distribution than its present range. The Odum tree provides hard, termite-resistant, all-purpose wood which is highly commercialized. 2.1.1 Botanical Description of Milicia excelsa Odum is a very tall deciduous tree, which can grow to about 60 meters high and 2.5 meters in diameter. It may have a straight cylindrical bole of about 30 meters before branching (FAO, 1986). However according to Brooks (1949), these dimension tend to be less in drier areas. The buttress is usually short and blunt, sometimes with root spurs and large exposed reddish brown lateral roots. 4
  • 5. In the young tree, the bark is smooth but later becomes rough and flaking. In the mature tree, the rough bark has reddish-brown conspicuous lenticels and slashes very gritty with brown spots and rapid watery latex. Venation on its lower surface looks like a sponge with conspicuous gaps in between the veins with lateral nerves up to 12 in maximum with a simple petiolate leaf (Hawthorne, 1990). The juvenile leaf is oblong-elliptic with serrate margin and densely covered with hair below the leaf (FAO, 1986). It is usually light green, soft and smooth to touch. However, as the tree grows, it puts on new leaves of different form – broad, ovate with darker colouring and less serrated edges which are shiner (white, 1966). 2.1.2 Ecology of Milicia excelsa Seedlings Milicia is a pioneer species. The seedling thus responds strongly to increase in irradiance. It cannot survive in deep forest shade but grows rapidly in full sun. Photoblasticity in the species accounts for its prevalence in more heavily disturbed forest, on road margins and on farms. The seedling shows greater investments in leaves. When it happens to occur in the under shade, it produces thin leaves with large surface area, while thick leaves are produced in high irradiance, having lower specific area. It has high leaf turn over in all light intensities (Swaine et al, 1997). Generally, it has high compensation and low saturation points. The common adversary to the seedling is Phytolyma spp which cause galls to be formed on the leaves. This disrupts the plants normal physiological processes, causing epical dieback, growth reduction and seedling mortality. The succulent young shoots are sometimes browsed by duikers and other animals (Irvine, 1961). The Milicia gall bug, Phytolyma spp are insects of the order Homoptera and the family Psyllidae. 5
  • 6. 2.2 Growth in Tropical Seedlings A seedling is a plant in which a significant proportion of its biomass is constructed from seed reserves, rather than from resources acquired auto-trophically (Kitajima, 1996). However, by convention, a seedling to a forester refers to a young plant of about 2.7 m (Whitmore, 1996). Seedlings are basically of two types, those that can do well under shade cover called shade tolerant and those that can only survive and grow well in the presence of light, called shade intolerant or pioneer species (Swaine et al, 1997). The growth of a tropical tree seedling in a particular environment and their ability to adapt to changes in that environment depend on the complex interaction of the morphological and physiological attributes of each species. The growth and development of a seedling is in stages. These stages are seed stage, seedling expansion stage, seedling seed- reserve stage, seedling autonomous stage and juvenile stage (Garwood, 1996). The tropical tree species exhibit high morphological diversity, but little is known about the functional significance of this morphological diversity (Kitajima, 1996). Initially the growth is primary and involves developments which terminate when direct derivatives of apical meristems becomes mature. This growth produces roots, stem and leaves in the seedling. Secondary growth which result from the activities of the vascular cambium, occur in the latter stages and is responsible for the thickening of both roots and stem (Kozlowski, 1971). 6
  • 7. 2.2.1 Growth of Milicia seedlings Growth can be defined as the increase in mass due to division and enlargement of cells and may be applied to an organism as a whole or any of its parts. All living organisms begin as a single cell, which usually divides and keeps dividing until possibly billions of cells are formed. As the various cells mature, they usually become larger and then differentiate. Thus, they develop different forms adapted to specific functions such as conduction, support or secretion of special substances (Stern, 1997). According to Levetin and McMahon (1999), apical meristems are located at the tip of all roots and stems and contribute to the increase in length of plants. Tissues that develop from these apical meristems are part of the primary growth of the plant and give rise to the leaves and non-woody stems and roots. Some plants have additional meristematic tissues that contribute to increases in diameter. These are the vascular cambium and cork cambium. Tissues developing from these are considered part of the plant secondary growth. 2.3 Factors Affecting Seedling Growth Seedling growth and development revolve round carbohydrate manufacture and utilization. Factors that influence the manufacture and utilization of carbohydrates and other biosynthetic processes, affect the growth. These factors include water, light, temperature, herbivory and other edaphic factors (Nwoboshie, 1982). 2.3.1 Water, Light and Temperature Of all the factors controlling seedling growth, water is the most critical. Water is the vehicle for all physiological and biochemical processes through which life is maintained. 7
  • 8. In the plant, opposing effect of transpiration and water absorption controls water. Whenever transpiration is greater than absorption, the plant becomes dehydrated. A decrease in hydration of protoplasm of cells in the meristematic tissues usually results in cessation or checking of cell division or cell enlargement or both. If there are no limiting growth factors, an increase in hydration of the protoplasm of a meristem usually results in an increase in the rate of cell division and the cell enlargement phase of tree growth. However, all phases of tree growth are not equally affected by the attenuation in the volume of water within the seedling (Nwoboshie, 1982). Light is the principal limiting factor for growth in all forests (Swaine et al, 1997). Light affects growth through its effects on photosynthesis. It affects photosynthesis in terms of its quality or wavelength composition, intensity or irradiance and duration. Light is important for many physiological processes such as stomatal action permeability, absorption of electrolytes as well as athocyanin and chlorophyll synthesis (Nwoboshie, 1982). Spatial variation in light availability leads to variation in other physical and biotic environmental factors such as temperatures, herbivore abundance and activities of pathogenic fungi and bacteria. Thus successful seedling establishment in the under story or light gaps hinges upon species- specific responses to these multiple factors confounded with light environment, not merely upon light intensity, spectral quality or sun flecks (Kitajima, 1996). Temperature affects plant growth through its effects on biochemical processes (Fitter and Hay, 1987). Physiological and biochemical processes in plants are catalyzed by enzymes which are active within certain temperatures range; hence plant can only growth within these temperatures ranges. In the tropics, this rage is between 150C and 360C. 8
  • 9. Within the range, the growth of some plants increases with temperature while it is opposite for other plants (Nwoboshie, 1982). 2.3.2 Herbivory Herbivory is the consumption of plant biomass or parts of plants by animals. The parts usually consumed are the fruits, seeds, leaves, twigs and buds. Mammals, birds and insect defoliators are normally responsible for this. Seedlings are more prone to herbivory and this may cause their early death or retard the growth of seedlings, though other factors may be favourable. The herbivores often prefer the young and fleshy leaves that may be rich in nutrients such as nitrogen, phosphorus and potassium. According to Hall and Swaine (1986) plants have defensive mechanisms to prevent being preyed upon. These mechanisms include hairs, phytotoxins and thorns, shedding of damaged leaves and high leaf turn over in short-lived leaves. Shade-tolerant seedlings appear to show greater defense and storage allocation than the pioneer or shade intolerant seedlings (Kitajima, 1996). 2.3.3 Edaphic Factors Although soil may vary considerably in structure and in physical, chemical and biotic properties, the rate of growth of a seedling is influenced by those properties of the soil. From the soil, the plant derives its nutrients and it is a storehouse for water and oxygen, all of which are necessary for the physiological processes associated with growth. 9
  • 10. Hence the relative abundance of these factors in a particular soil, determine the rate at which the seedling will grow on the soil (Brady, 1990). 2.4 Plant Fertilization Fertilizer is any substance which is incorporated into the soil to increase crop growth and yield by providing one or more of the elements essential for plant growth. Fertilizers are applied to promote healthy growth, assist plants to overcome adverse effects of diseases or insects or to correct mineral deficiencies, increase growth rate and maintain satisfactory vigor (Evans, 1992). Fertilizer can be applied anytime during the growing season if a seedling’s leaves turn yellowish, experience extreme slow growth or some other signs. If fertilizers are to be applied under hot, dry conditions, it is important to water the seedlings soon after the fertilizer application so that the salt from the fertilizer does not damage the seedling root system (Swanson, 2000). Plants need a number of essential elements to enable them to grow and reproduce. These elemental nutrients may be classified as micronutrients and macronutrients. The macronutrients (primary nutrients) include Nitrogen (N), Phosphorus (P) and Potassium (K). Plants need these elements in relatively large quantities for their metabolism processes. The most important of the macronutrients is Nitrogen (N) which is the most limiting nutrient in the soil. It is generally known that nitrogen determines the yield of most crops more than any other nutrient element provided there is adequate rainfall or water supply (Halley, 1982). 10
  • 11. The micronutrients Copper (Cu), Zinc (Zn), Manganese (Mn), Boron (B), Molybdenum (Mo), Iron (Fe), Chlorine (Cl), Calcium (Ca), Magnesium (Mg) and Sulphur (S) are needed in relatively small amounts and are generally found in sufficient quantities in normal pH balanced soils. However, a deficiency in any of these nutrients can affect the health of seedlings. The macronutrients have a role in building the structure of plants, whereas micronutrients are important in enzyme systems and contribute to the plants function rather than its structure (Halley, 1982; Brian and West, 1996). 2.5 Organic Fertilizer Organic fertilizers are obtained from living sources, an example is manure. The most noteworthy advantage of organic fertilizers is the fact that they are mostly insoluble and therefore are slower to release nutrients to plants. This reduces the leaching effect that results from most chemical fertilizers that causes so many problems (Zublena, 1996). Organic fertilizers also help to improve soil quality. The consistent use of chemical fertilizers creates plant life dependent upon synthetic fertilization as these fertilizers only work at the plant level. Through the introduction of organic matter and resulting improvement of the soil and stimulation of the soil microbial activity, an environment can be created to support plant life and provide a slow and consistent flow of nutrients to the plants. Organic fertilization is one of the options for creating a long lasting and healthy plant-soil environment that is ecologically responsible and economically viable for long term run (Hileman, 1972). 11
  • 12. 2.5.1 Poultry Manure Poultry manure is described as dropping from birds, which are kept domestically, especially chickens. Chicken manure is the richest animal manure in terms of N, P and K (Russell, 1998). According to Hileman (1972), poultry manure is an excellent source of nutrients that can be used in most fertilizer programs. The growth of the poultry industry in Ghana and the corresponding increase in quantity and availability of poultry manure as well as its associated environmental hazards has made it prudent to put poultry manure into an efficient use such as raising seedlings in the nursery. Poultry manure has been found to be environmentally safe source of fertilizer than inorganic fertilizer. Studies carried out to investigate the residual effects of inorganic fertilizer on soil, destroyed soil organic and increased pests and disease activities. The management of poultry manure can be a valuable source of nutrients for plants and still ensure the safety of the environment (Brady, 1984). 2.5.2 Nutrient Value of Poultry Manure Poultry manure is the most valuable of all manures produced by livestock. It has been used as a source of plant nutrients and as a soil amendment. The type and amount of nutrients in poultry manure and the nutrients’ eventual availability to plants may vary considerably (Halley, 1982). Some factors affecting nutrient value of applied poultry manure include: type of ration fed, method of collection and storage, amount of feed, bedding and/or water added, time and method of application, soil characteristics, the crop to which manure is applied and climate (Halley, 1982; Zublena et al., 1993). Hileman (1972) described poultry manure as organic manure with high fertilizer value which is successfully used on wide variety of crops as a valuable source of plant food. Increasing levels of various harmful elements (copper and arsenic) and inorganic salts (sodium, calcium, potassium and magnesium) in feed will 12
  • 13. increase their concentrations in manure. There is concern about the potential toxic effects to plants of high concentration of heavy metals and salts in soil, as a result of high application rates of manure to the land. Generally, as the percent moisture of animal waste material decreases, the percent nutrient content increases (Gale, 1997). Table 2.1 the Percentage Composition of Poultry Manure Manure Organic matter Ash N P 2 O5 K2O Fresh manure 80 20 6.0 4.0 2.0 Dry matter) Old manure 65 35 3.5 6.0 2.8 (Dry matter) Source: Smith (1962). About 30 percent of the total nitrogen in fresh manure is in the form of undigested food residues; the remaining 70 percent is urinary nitrogen consisting of nearly 10 percent as ammonium compounds and 60 percent as uric acid (Table 2.1). The faecal nitrogen is relatively stable, but uric acid is a very high unstable compound in moist conditions and will change into urea and ammonium salts even at fairly low temperatures. The loss of nitrogen is only about 10 percent if fresh manure is dried quickly at a high temperature. It is best therefore to spread manure directly on the field in wet weather; the rain facilitates the incorporation of ammonia and soluble nitrogen compounds into the soil, where they are absorbed and speedily converted into nitrates (Smith, 1962). 13
  • 14. 2.5.3 Positive Effects of Poultry Manure The effect of farmyard manure on humus is evident in the tropics. Agboola et al. (1975) reported that a moderate application of manure on crop soils in the rainforest zone was sufficient to slow down humus decomposition, which progress only half as fast as with mineral fertilizers. The sorption power; that is the soil’s capacity to store and release nutrients is also improved by manure application. Significant results have been obtained when manure was applied to wetland rice (Müller-Sämann and Kotschi, 1994). Manure also aids in reducing the incidence of some plant diseases. Mathur and Sinha (1966) studied the influence of manuring on seedling-rot, root-rot and wilt of guar and found that the incidence in all the cases was considerably reduced in manured soil. The reduction in disease incidence was attributed to the increased plant vigour resulting from the high nutritive status of the manured soil. 2.5.4 Potential Harmful Effects of Poultry Manure In areas of intense poultry production, over fertilization of land with poultry manure occurs. The result is suspected groundwater and surface water problems as excess nutrients run-off the land or leach into groundwater supplies. Fresh stable manure is prone to form organic acids. These are rapidly processed by soil organisms, which can lead to an overload of oxygen and nitrogen in freshly manured soils (Gale, 1997). The C/N ratio of fresh manure is often too high. This can result in a temporary N block such that hardly any nitrogen from manure will be available in the following period. Manures are also costly per unit of plant food (Halley, 1982; Müller-Sämann and Kotschi, 1994). 14
  • 15. CHAPTER THREE RESEARCH METHODOLOGY 3.1 Study Area The experiment was conducted at the Faculty of Renewable Natural Resources Demonstration Farm (KNUST-Kumasi). This area falls within Moist Semi-deciduous Vegetation Zone of West Africa. The area is characterized by a bimodal rainfall pattern with the major wet season between May and July. This area experiences a short dry season in August and a long one between December and March. The annual rainfall of the area ranges between 1250 mm -1500 mm. The soil in the study site belongs to the family Ferric Acrisols in the soil taxonomy. Ferric Acrisols are loamy sand, well drained but strongly acidic (Adu and Asiamah, 1992). 3.2 Research Design The experimental design used in this field experiment was a Randomized Complete Block Design. The randomized complete block design is one of the most widely used experimental designs in natural resources research. Blocking is done to reduce experimental error by eliminating the contribution of known sources of variation among experimental units (Nkyi, 2009). Two-month old Milicia excelsa seedlings were obtained from the Forestry Research Institute of Ghana (FORIG), Kumasi-Ghana. The poultry manure was obtained from the Animal Science Department of the Faculty of Agriculture (KNUST-Ayeduase). Other tools and equipment used included cutlass, rake, watering can, tape measure, hand fork and hoe for the preparation of the planting bed. 15
  • 16. The plant parameters measured were the height (cm), stem diameter (mm) and the number of leaves. According to Mohr and Schopfer (1995), height and stem diameter are some of the frequently used methods of measuring the growth of multi-cellular living systems and often advantageous to use several characteristics for the same system. Leaves are also an important part of plants; they help in the process of photosynthesis. Leaves have their own definite shape and arrangement according to requirements of the plant. Leaves trap energy from sunlight and convert it into pure compounds. Leaves were counted visually. An electronic caliper was used in measuring the stem diameter while the height was measured with a meter rule. Data on the height, stem diameter and number of leaves were collected two days after transplanting and then fortnightly over the twelve weeks of the research. The experiment was conducted from 23rd November, 2010 to 19th February, 2011. 3.2.1 Experimental Design and Layout The experimental design used was a Randomized Complete Block Design. The study was carried out in three blocks, each block consisting of five plots (Figure 3.1). The poultry manure was applied at the rate of 17,500 kg/ha as recommended by Zublena et al., (1993). Five levels of the poultry manure were used for the experiment. T1 (0.0 Kg), T2 (0.90 Kg), T3 (1.80 Kg), T4 (2.70 Kg) and T5 (3.60 Kg) 16
  • 17. BLOCK 1 BLOCK 2 BLOCK 3 Plot 1=T2 Plot 1=T2 Plot 1=T3 Plot 2=T4 Plot 2=T5 Plot 2=T2 7.0 m Plot 3=T1 Plot 3=T4 Plot 3=T5 Plot 4=T5 Plot 4=T1 Plot 4=T4 Plot 5=T3 Plot 5=T3 Plot 5=T1 1.0 m 0.5 m 1.0 m 0.5 m 1.0 m Figure 3.1 RCBD Experimental layouts with the allocated treatment. 3.2.2 Experimental Procedures Three beds representing the blocks of size 1.0 m × 5.0 m (5.0 m2) each and plots with dimensions of 1.0 m × 1.0 m (1.0 m2) were constructed with spacing of 50 cm between the blocks and plots making the total plot length of 7.0 m with an area of 7.0 m 2. The various treatments were randomly allocated to the plots (Fig 3.1) with eight seedlings per plot. Reference points of 1cm above the soil surface of the seedlings were marked with non- poisonous indelible ink to provide consistency at the point of the height and diameter measurement. The total number of experimental plots was fifteen. The poultry manure was applied at the rate of 17,500 Kg/ha as recommended by Zublena et al., (1993). Rates of poultry manure application were therefore applied based on the following calculation; 10000 m2 (1 hectare) = 17500 Kg. 1.0 m 2 X17500 Kg 1.0 m2 (plot size) = = 1.75 Kg/plot ≈ 1.80 kg/plot (average application). 10000 m 2 17
  • 18. The recommended rate per plot was halved, doubled and multiplied by one-half to achieve the various treatment levels. Five levels of the poultry manure were used for the experiment. T1 (0.0 Kg, control), T2 (0.90 Kg, halved), T3 (1.80 Kg, recommended rate per plot), T4 (2.70 Kg, multiplied by one-half) and T5 (3.60 Kg, doubled). The poultry manure was applied to the soil two weeks before transplanting the seedlings to the experimental plots to allow the ammonia to be nitrified so that it will not burn the young plants as recommended by Smith (1962). 3.3 Cultural Practices on the Experimental Plots Seedlings were transplanted from the poly bags when they were two months old. The transplanting exercise was undertaken late in the afternoon after the bed had been watered thoroughly. According to Hilary (2009), the best time of day to plant is in the late afternoon when the sun is not so hot. By taking advantage of this time of day, the new plants are able to acclimatize overnight. Strong sun and wind have a potentially adverse effect on new transplants and unless watered carefully, and in some cases sheltered from the wind and sun, they can severely wilt. This places the plants under stress at the very beginning of their growing cycle. This is not a good idea because sometimes they never bounce back and do not thrive as well as they could have. Watering of the transplanted seedlings was done immediately after transplanting and twice daily and evenly with each plot receiving about the same volume of water. Plots were not watered after heavy rains due to high incidence of fungal infestation when the plant roots are overwatered (Swanson, 2000). 18
  • 19. Weeds that appeared on the beds were controlled by hand-picking to prevent competition for water, nutrients, space and light. Weeds that appeared between the beds were hoed to eliminate any type of competition. According to Townsend and Sinden (1999), weeds host pests and diseases that can spread to cultivated crops. Weeds also impose costs on producers in two ways; through reductions in the quality and quantity of yields, and increases in input requirements for weed control. This cost may have economic consequences for the wider community if a large number of farmers are affected, leading to variations in supplies and prices of commodities. 3.4. Data collection An indelible ink was used to mark each seedling 1cm above the soil, where the diameter and height readings were taken so that irregularity of the soil around the seedlings would not affect the recording. Initial measurements of both the heights and the diameters were taken two days and two weeks after transplanting and application of the treatments respectively. Subsequent readings were taken every two weeks for a period of three months within which seven readings were recorded. 3.5 Data Processing and Analysis All data collected were subjected to a one-way Analysis of Variance (ANOVA). Microsoft excel was used to compute the increment of the various plant parameters measured. Least Significant Difference (LSD) was used to separate treatment means that differed significantly. Any treatment mean with a difference more than the calculated Least Significant Difference was interpreted as significant and ascribed ** and those without any ns significant difference were ascribed . 19
  • 20. This was done for all the plant growth parameters measured with the exception of the survival percentage. Coefficient of Variation was used to ascertain the acceptance of the experiment as recommended by Nkyi (2009) that the Coefficient of Variation should not be greater than 20 percent, otherwise the number of blocks should be increased or the experiment rejected. (Observed value - Expected value) 2 The Chi-Square (X2) method with the formula: X2 = { } Expected value was used to determine the significance of the poultry manure on the seedling percentage of survival at a significant level of 5%. A Chi- Square value higher than the calculated value renders the effect insignificant and vice versa. The results are represented using appropriate graphs and tables. 20
  • 21. CHAPTER FOUR RESULTS 4.1 Height measurements of Milicia excelsa seedlings Almost all the treatments T1 (0.0 Kg) T2 (0.90 Kg), T3 (1.80 Kg), T4 (2.70 Kg) and T5 (3.60 Kg) showed increment in height throughout the experimental period. However, Treatment (T1) and Treatment T5 showed a decrease in height in the eighth week with Treatment T1 recording the minimum increment in height and Treatment T4, the highest increment in height, (Fig.4.1). The experiment showed that, from the 2nd to the 6th week there were low increments in height for all the treatments. Treatment T1 and Treatment T5 had the same increment within the first four weeks. However Treatment T1 had a decrease in height between the 6th and 8th week. From the 10th to the 12th weeks, Treatment T4 recorded the highest mean height increment (Fig 4.1). The Analysis of Variance (ANOVA) carried out indicated that the treatments were significantly different at 5% level of significant on mean height increment of the seedlings (F0.05, 4, 8= 8.40 ≥ F0=3.84). Least Significant Difference (LSD) analysis revealed that, there were significant differences between T1 (0kg) and each of T2, T3, T4 and T5 but no significant difference among T2 and T3, T5 as well as between T3 and (T4 and T5). It was observed that there is a drastic decrease in the height increment between week 6 and week 8 The initial mean height increment for all the treatment levels recorded after fertilization were; T1= 9.17 cm, T2= 9.88 cm, T3= 10.13 cm T4= 9.70 cm, T5= 10.00 cm as against 19.25 cm, 23.72 cm, 25.19 cm, 30.28 cm and 24.00 cm for treatments T1, T2, T3, T4, and T5, 21
  • 22. respectively as the values recorded at the time the experiment was terminated on 19th February, 2011. 9 8 Height increment (cm) 7 T1 6 T2 5 4 T3 3 T4 2 1 T5 0 Week 2 Week 4 Week 6 Week8 Week 10 Week 12 Weeks after transplanting Fig 4.1 Mean Height increments of Milicia excelsa seedlings. 4.2 Diameter measurements of Milicia excelsa seedlings Diameter increments were observed for all the treatments throughout the experiment period, (Fig 4.2). For the first six weeks after the application of the treatments, the increments were high for all treatments except treatment T5 which had a low increment of 8.69 cm. The increments for all the treatments decreased from the 8th to the 10th week. There were steady increments for treatments T1, T3 and T4 between week 10 and week 12 while treatments T2 and T5 were not significantly different. Treatment T4 had the highest mean increment followed by T3 and T2 with treatment T1 recording the least mean diameter increment. The results of the Analysis of Variance (ANOVA) showed that, all the treatments had no significant effect on the diameter increments of the seedlings at a significant level of 5% 22
  • 23. (F0.05,4,8 = 3.74 ≤ F0 = 3.84). Least Significant Difference (LSD) showed that, there were significant differences between T1 (0.0 Kg) and T4 (2.70 Kg), and treatments T4 and T5 (3.6 Kg) but no significant difference among T1 and each of T2 (0.9 Kg), T3 (1.80 Kg), and T5. Again, there were no significant difference among T2, T3 and T4. 1.2 Diameter increment (mm) 1 T1 0.8 T2 0.6 T3 0.4 T4 0.2 T5 0 Week 2 Week 4 Week 6 Week8 Week 10 Week 12 Weeks after transplanting Fig.4.2 Mean diameter increments of Milicia excelsa seedlings. 4.3 Mean Number of Leaves of Milicia excelsa seedlings All the treatments showed increment in mean number of leaves throughout the experimental period. However, Treatment T1 (0.0 Kg) showed the lowest increment and Treatment T4 recorded the highest increment, (Fig.4.3). The experiment showed that, from the 2nd to the 6th week low increments were recorded for all the treatments, (Fig 4.3). Between the 6th and 10th week, there were steady increments of the mean number of leaves for Treatments T2 (0.9 Kg), T3 (1.80 Kg), T4 (2.70 Kg and T5 (3.60 Kg) while Treatment T1 still remained almost the same as the first six weeks. 23
  • 24. From the 10th to the 12th week, the mean number of leaves remained the same for all the treatments except treatment T4. Analysis of Variance (ANOVA) at 5% significance level showed that poultry manure had a significant effect on mean number of leaves (F0.05, 4, 8= 48.81 ≥ F0=3.84). Least Significant Difference (LSD) showed that, there were significant differences between almost all the treatment means but no significant difference among T1 and each of T2, and T3 as well as between treatment T3 and treatment T4. The mean number of leaves at the end of the study period were T1=7.67, T2=7.67, T3=10.00, T4=19.67 and T5=14.0 18 16 T1 14 Mean Number of Leaves 12 T2 10 T3 8 6 T4 4 T5 2 0 Week 2 Week 4 Week 6 Week 8 Week 10 Week 12 Weeks After Transplanting Fig.4.3 Mean Number of Leaves of Milicia excelsa seedlings. 4.4 Percentage Survival of Milicia excelsa seedlings Three months after transplanting, the percentage survival of the Milicia excelsa seedlings ranged from 87.50% to 100% (Fig4.4). There were significant differences in the rate of survival between the various treatments with a survival expectancy of 60% (x²=30.74 > 24
  • 25. 23.70, p=0.05). All the treatments recorded no mortality during the first six weeks after transplanting. However, treatment T1 recorded three plants mortality representing 12.50 percentage of mortality in the eighth week. All other treatments recorded mortality as low as zero percent. The total mortality over the entire study occurred in the first eight weeks. There was no mortality after 8 weeks of the experimental period and all the treatments (T2, T3, T4, and T5) except treatment T1 had the same percentage survival of 100 percent throughout the study period. 102 100 98 Percentage Survival 96 94 92 90 88 86 84 82 80 T1 T2 T3 T4 T5 Treatments Fig.4.4 Percentage survival of Milicia excelsa seedlings 25
  • 26. CHAPTER FIVE DISCUSSION 5.1 Height increments of Milicia excelsa seedlings All the treatments increased in height throughout the study period, Fig 4.1. Analysis of Variance (ANOVA) tested at 5% significance level showed a significant effect of poultry manure on the mean height increments. However, the degree of increment varied among the treatments. There was low height increments recorded for all the treatments between the 2nd and 6th weeks and even a decrease in seedling height increment for the 8th week. This might be due to the fact that the poultry manure applied had not yet fully decomposed to reach the roots of the seedlings for it to be absorbed. Therefore the little fertility in the soil was then used by the seedlings. The significant increase in the height of the Milicia excelsa seedlings might be due to the nutrient contribution from decomposing poultry manure. The effect of T4 (2.7 Kg of manure) was greater than that of T1 (0 Kg of manure). This revealed a sharper growth with increasing rate of manure application. This confirms the assertion by Duryea and Brow (1984) that seedlings grown at fairly higher fertilization levels produced higher growth rates. From the 8th to the 10th week, there were steady and sharp increases in heights for T1, T4 and T5; however, T2 and T3 almost had a constant stem increment. Smith, (1962) reported that poultry manure may be of little immediate value in correcting nutrient deficiencies since it takes time for it to decompose and release nutrients to plants roots. The role played by the three primary nutrients (N P K) is vital in the process of plant development. 26
  • 27. The significant increase in the height of the seedlings might be due to the nutrient contribution from decomposing poultry manure. The application of 2.7 Kg of manure T4, performed better than when 0.9 Kg of manure T2 was applied. The performance of T4 (2.7 Kg of manure) could be attributed to the increased supply of nitrogen (N). This might have increased the meristematic and development activities through the differentiation of tissues and have therefore increased growth with respect to the height of the seedlings. This result confirms the findings of Mohan and Sharma (1992) who worked on the effect of nitrogen and sulphur on the growth and yield of mustard seedlings. Hileman (1972) described poultry manure as organic manure with high fertilizer value which is successfully used on a variety of crops. Zublena et al. (1993) also noted that the organic matter in soil improves moisture and nutrient retention. These properties of high fertilizer value, improvement in moisture and nutrient retention helped in increasing the rate of growth and subsequently produced viable and healthy seedlings that can withstand adverse weather conditions. Therefore the presence of these nutrients in sufficient amounts resulted in vigorous growth of the seedlings. From the 10th to 14th week, the mean height increments continued to increase for all the treatments except for T1. Organic fertilizers are one of the options for creating a long lasting and healthy plant-soil environment that is ecologically responsible and economically viable for long term supply of nutrients for plant growth and development (Gale, 1997). 27
  • 28. The research alternate hypothesis for this research that different levels of poultry manure would provide environmental conditions favourable for the growth, development Milicia excelsa seedlings is therefore accepted and the null hypothesis rejected. 5.2 Diameter increments of Milicia excelsa seedlings All the treatments (T1, T2, T3, T4 and T5) had no increasing effect on the seedling stem diameter throughout the study period according to the Analysis of Variance (ANOVA) tested at 5% significance level of the Milicia excelsa seedlings. Also, the degree of increment varied among the treatments with T1 being the least and T4 as the highest. Low increments in diameter were recorded for all the treatments between the 2nd and 6th week. This might be due to the fact that the poultry manure applied was being used for apical meristematic growth. Initially the growth is primary and involves developments which terminate when direct derivatives of apical meristems becomes mature. This growth produces roots, stem and leaves in the seedling. Secondary growth which result from the activities of the vascular cambium, occur in the latter stages and is responsible for the thickening of both roots and stem diameter (Kozlowski, 1971). 5.3 Mean Number of Leaves of Milicia excelsa seedlings All the treatments showed increment in mean number of leaves throughout the experiment period. However, Treatment one T1 showed the minimum increment and Treatment T4 recorded the highest increment, (Fig.4.3). Analysis of Variance (ANOVA) at 5% significance level showed a significant effect of poultry manure on the mean number of leaves. 28
  • 29. This significant increment might be due to the availability of nutrients for plant growth especially in the leaf tissues. This confirms the assertion by Kozlowski (1971) that the initial growth of seedlings is primary and involves developments which terminate when direct derivatives of apical meristems becomes mature. This growth produces roots, stem and leaves in the seedling. Secondary growth which result from the activities of the vascular cambium, occur in the latter stages and is responsible for the thickening of both roots and stem diameter. The alternate hypothesis for this research that different levels of poultry manure would provide environmental conditions favourable for the growth, development Milicia excelsa seedlings is again accepted and the null hypothesis rejected. 5.4 Percentage Survival of Milicia excelsa seedlings. Three months after transplanting, the percentage survival of the Milicia excelsa seedlings ranged from 87.5 to 100 percent (Fig4.4). According to a Chi-Square (x2) test carried out it revealed that, there was a significant effect of the poultry manure applied to the seedlings with a survival expectancy of 60 percent at significant level of 5%. All the treatments (T1, T2, T3, T4 and T5) recorded no mortality during the first six weeks after transplanting. However, three mortalities of plants were recorded during the first 8 weeks representing about 12.50% of mortality in the eighth week for treatment T1. All other treatments recorded mortality of 0%. The total mortality over the entire study occurred in the first eight (8) weeks with only one plant dead. This might be due to low 29
  • 30. supply of water to the seedling growth and development during the dry season of the research. Nwoboshie, (1982) reported that of all the factors controlling seedling growth, water is the most critical. Water is the vehicle for all physiological and biochemical process through which life is maintained. Whenever transpiration is greater than absorption, the plant becomes dehydrated. A decrease in hydration of protoplasm of cells in the meristematic tissues usually results in cessation or checking of cell division or cell enlargement or both. No mortality was encountered after the first 8 weeks throughout the three months of the study period. The percentage of the seedling survival may be as a result of the improved level of the soil nutrient for the plant growth, development and survival. The alternate hypothesis for this research that different levels of poultry manure would provide environmental conditions favourable for the growth, development and survival Milicia excelsa seedlings is accepted and the null hypothesis rejected. 30
  • 31. CHAPTER SIX CONCLUSIONS AND RECOMMENDATIONS 6.1 Conclusions 6.1.1 Effect of poultry manure on vegetative growth of Milicia excelsa seedlings The study indicates that poultry manure is a valuable fertilizer because application of the poultry manure resulted in a significant effect on the mean stem height of Milicia excelsa seedlings. However, there was no significant effect on the species diameter. 6.1.2 Effect of poultry manure on the percentage survival of Milicia excelsa seedlings Again the poultry manure had a significant effect on the percentage survival of the Milicia excelsa seedlings. An application rate of 27000 Kg/ha was capable of enhancing the survival of the Milicia excelsa seedlings by 87.50 percent over the control. 6.1.3 Effect of poultry manure on the mean number of leaves of Milicia excelsa seedlings Poultry manure also had a significant effect on the mean number of leaves and can therefore be applied to Milicia excelsa seedlings for raising healthy and good seedlings in the nursery as well as for its plantation establishment. 31
  • 32. In general, the introduction of Milicia excelsa into plantations by enhancing its early growth performance could have beneficial effects on the forest of Ghana, since it will reduce the high dependency on the forest for Milicia excelsa species for subsistence or commercial purposes. 6.2 Recommendations Since the poultry manure significantly increased the growth of the Milicia excelsa seedlings, their application should be encouraged for the production of strong and healthy seedlings for plantation purposes with a recommended rate of 27,000Kg/ha. This will serve as a substitute for inorganic fertilizers thereby reducing cost of inputs for the farmer. It may be worthwhile considering the application of poultry manure in the early stages of seedling nursing so as to reduce plant shock during transplanting. Further research should be carried on the seedlings for a long period of time of about thirteen to fifteen months, so as to ascertain the findings obtained from this research work. 32
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  • 37. APPENDICES APPENDIX 1 Analysis of Variance (ANOVA) for Poultry Manure on the Mean Stem Height of Milicia excelsa seedlings Sources of Variation Sum of squares Degree of Freedom Mean sum of squares F0 F-critical Treatment 216.78 4 54.20 8.40** 3.84 ns Blocks 53.80 2 26.90 4.17 4.46 Residual 51.61 8 6.45 Total 322.19 14 ns **Significant at α = 5% Not significant at α = 5% C.V = 10.00% APPENDIX 2 Least Significant Difference (LSD) for Mean Stem Height at 5% Significance level Least Significant Difference Treatment Means Differences in Treatment Mean 4.790 y₁=19.25 y₁ - y₂=19.25-24.05= 4.80* y₂=24.05 y₁ - y₃=19.25-27.53= 8.28* y₃=27.53 y₁ - y₄=19.25-30.70= 11.45* y₄=30.70 y₁ - y₅=19.45-25.45= 6.20* ns y₅=25.45 y₂ - y₃=24.05-27.53=3.48 y₂ - y₄=24.05-30.70= 6.65* y₂ - y₅=24.05-25.45= 1.40ns y₃ - y₄=27.53-30.70= 3.17ns y₃ - y₅=27.53-25.45= 2.08ns y₄ - y₅=30.70-25.45= 5.25*  * = Significant at 5% Significance level. y₁=T1, y₂=T2, y₃=T3, y₄=T4, y₅=T5  ns= Not significant at 5% Significance level. 37
  • 38. APPENDIX 3 Analysis of Variance (ANOVA) for Poultry Manure on the Mean Number of Leaves of Milicia excelsa Seedlings. Sources of Variation Sum of squares Degree of Freedom Mean sum of squares F0 F- critical Treatment 312.4 4 78.10 48.81 * 3.84 Blocks 1.20 2 0.60 0.38ns 4.46 Residual 12.80 8 1.60 Total 326.40 14 ns **Significant at α = 1% Not significant at α = 5% C.V = 10.68% APPENDIX 4 Least Significant Difference (LSD) for Mean Number of Leaves at 5% Significance level Least Significant Difference Treatment Means Differences in Treatment Mean 2.390 y₁=7.67 y₁ - y₂=7.67-7.67=0.00ns y₂=7.67 y₁ - y₃=7.67-10.00= 2.33ns y₃=10.00 y₁ - y₄=7.67-19.67= 12.00* y₄=19.67 y₁ - y₅=7.76-14.00= 6.33* y₅=14.00 y₂ - y₃= 7.67-10.00= 2.33ns y₂ - y₄=7.67-19.67= 12.00* y₂ - y₅=7.67-14.00=6.33* y₃ - y₄=10.00-19.67= 9.67* y₃ - y₅=10.00-14.00= 4.00* y₄ - y₅=19.67-14.00= 5.67*  * = Significant at 5% Significance level. y₁=T1, y₂=T2, y₃=T3, y₄=T4, y₅=T5  ns= not significant at 5% Significance level. 38
  • 39. APPENDIX 5 Analysis of Variance (ANOVA) for Poultry Manure on the Mean Stem Diameter of Milicia excelsa Seedlings Source of Variation Sum of Squares Degrees of Freedom Mean Sum of Squares F0 F- critical ns Treatment 2.66 4 0.665 3.74 3.84 Blocks 4.21 2 2.107 11.84** 4.46 Residual 1.42 8 0.178 Total 8.30 14 ns **Significant at α = 1% Not significant at α = 5% C.V = 10.58% APPENDIX 6 Least Significant Difference (LSD) for Mean Stem Diameter at 5% Significance level Least Significant Difference Treatment Means Differences in Treatment Mean 0.796 y₁=3.66 y₁ - y₂=3.66-4.05= 0.39ns y₂=4.05 y₁ - y₃=3.66-4.14= 0.48ns y₃=4.14 y₁ - y₄=3.66-4.68= 1.02* y₄=4.68 y₁ - y₅=3.66-3.46= 0.20ns ns y₅=3.46 y₂ - y₃=4.04-4.14= 0.09 y₂ - y₄=4.04-4.68=0.63ns y₂ - y₅=4.04-3.46=0.59ns y₃ - y₄=4.14-4.68= 0.54ns y₃ - y₅=4.14-3.46=0.68ns y₄ - y₅=4.68-3.46=1.22*  * = Significant at 5% Significance level. y₁=T1, y₂=T2, y₃=T3, y₄=T4, y₅=T5  ns = not significant at 5% Significance level. 39