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RESEARCH PAPER OPEN ACCESS
Effect of some abiotic factors on the concentration of β-
sitosterol of Prunus Africana (Hook.f.) Kalkman in the tropical
forests of Cameroon
Maurice Tchouakionie1*
, Emmanuel Youmbi2
, Michel Ndoumbe Nkeng3
, Siméon
Fogue Kouam4
, Marc Lamshôft5
, Michael Spiteller5
1
Laboratory of Plant Biotechnology and Environment, Department of Plant Biology, Faculty of
Science, University of Yaounde I, P.O. Box: 812 Yaounde, Cameroon
2
Department of Plant Biology, Faculty of Science, University of Yaounde I, P.O. Box: 812 Yaounde.
Cameroon
3
Institute of Agricultural Research for Development (IRAD) Yaounde. P.O. Box: 2123 Yaounde,
4
Department of Chemistry, Higher Teachers’ Training College, University of Yaounde 1, P.O. Box
47 Yaounde, Cameroon
5
Institute of Environmental Research (INFU), Department of Chemistry and Biology, Chair of
Environmental Chemistry and Analytical Chemistry, TU Dortmund Otto-Haln-Sir 6 D-14221
Dortmund, Germany
Article published on February 25, 2014
Key words: Prunus africana, phenotypic character, soils, β-sitosterol, altitude.
Abstract
Prunus africana is a medicinal plant which develops in the mountains of several African countries. β-sitosterol can be used as a
marker for the control of the product quality of the aforementioned plant in terms of phytotherapy. Farmers and public
authorities do not have information on the influence of altitude and chemical characteristics of soils on the concentration of β-
sitosterol of P. africana. To contribute to solve the problem, this research, carried out in Cameroon, aims to appreciate the
effect of abiotic factors on the above phenotypic character. In nine composite samples of barks taken at different altitudes, the
concentration of β-sitosterol is appreciated via qualitative analyses by Thin Layer Chromatography, High Performance Liquid
Chromatography and quantitative analyses by Gas Chromatography coupled with the Mass Spectrometry. The chemical
analyses of soils taken under the stems of the aforementioned trees were made. The statistics were carried out using the SAS
software. The concentration of β-sitosterol in each population of P. africana varies from zero to 38.65 µg/ml. There is
variability between the averages of the aforementioned concentration with respect to altitude and chemical elements of the soils
but the differences are not significant. The Ascending Hierarchical Clustering distributes populations into three groups. These
tools obtained are indispensable for the ground management, the products exploited from this tree species and the production
of seeds for creating forest and agro-forest plantations.
* Corresponding Author: Maurice Tchouakionie  tchouakionie@yahoo.fr
International Journal of Agronomy and Agricultural Research (IJAAR)
ISSN: 2223-7054 (Print) 2225-3610 (Online)
http://www.innspub.net
Vol. 4, No. 2, p. 1-11, 2014
Tchouakionie et al. Page 2
Introduction
Prunus africana (Hook. F.) Kalkman is a medicinal
plant which develops in the forests of mountains at
altitudes going from 700 m to more than 1000 m in
several countries of Africa (Avery et al., 2001). Its
bark is exploited and marketed internationally
because of its effectiveness in the treatment of benign
prostates and hyperplasia (Watt and Bryer, 1962,
Bankill, 1997, cit. by Hall et al., 2000).
In pecuniary terms of value, one Kilogram of rough
bark is bought at 300 F CFA from farmers and the
drawn extract from the aforesaid Kilogram costs 500
000 F. CFA in pharmaceutical industries (Vockins,
2000, cit. Avana et al., 2006).
P. africana is a component of biodiversity which
represents 6 % of the species used for forest and agro-
forest plantations in the agro-ecological zone of the
high plateaus of the West of Cameroon (Tchouakionie
et al, 2010).
To optimize the output of the plantations, it is
necessary to take into account the biotic and abiotic
factors relating to the P. africana. The small farmers
and public authorities do not have formal information
on the variability of the concentration of β-sitosterol,
the principal active matter of P. africana with respect
to altitude and the chemical characteristics of the
soils of the aforementioned species plantations.
The general objective of this study is to appreciate the
effect of some abiotic factors on the concentration of
β-sitosterol of P. africana within mount Cameroon
and the Bamenda high land areas. To achieve this
goal, three specific objectives were formulated:
To evaluate the effect of altitude on the concentration
of β-sitosterol of P. africana;
to appreciate the correlation between the chemical
characteristics of the soils and the concentration of
β-sitosterol of the aforementioned species;
to group the populations of P. africana according to
their concentration in β-sitosterol.
In the biological context, P. africana belongs to the
family of Rosaceae and are found practically only on
mountains (Letouzey, 1982).The detailed description
of the adult tree is materialized by characteristic
phytogenetic parts (fig. 1).
The stem (Fig.1.A) is a seed-bearer in an agro-
ecosystem in Akum, within Mezam Division, in the
North-West of Cameroon. The base of trunk presents
a simple footing of 8-10 cm (Fig.1. B). The young
seedlings are visible under this tree. These seedlings
come from two modes of pollination in particular:
self-fertilization and cross-pollinated parents.
Pollination here is primarily entomophilous. However
the implication of certain birds was noted (Avana,
2006). Flowering is irregular in P. africana and
occurs every 2 to 3 years. Fructification intervenes 2
to 3 months after the beginning of flowering. The
number of fruits per inflorescence varies from 1 to 6
units (Fig. 1.C).
The natural ecological zone of P. africana in
Cameroon is confined to the mountain and sub-
mountain forests of altitudes ranging between 1500-
3000 m (Vivien and Faure, 2011). The surface
distribution of the forests of P. africana planted from
1976 to 2007, reached 625 ha with at least 1.526.430
trees (Kadu et al., 2012). The peasants partly receive
seeds from non-governmental organizations and
official establishments.
Concerning the influence of biotic factors on the
development of P. africana, analyses carried out by
Dawson and Powell (1999) using molecular markers
indicated that the variation is quite effective at the
level of the genes (fig. 2).
There are quantitative and qualitative differences in
chemical compounds from the barks of P. africana
within geographically dispersed populations (Hall et
al., 2000). The concentration of β-sitosterol, the
major component of the bark of P. africana, varies
from 101 to 150 µg/ml between origins and 50 to
191µg/ml between individuals (Simons and Leakey,
2004, cit. Avana, 2006). One of the factors of the
Tchouakionie et al. Page 3
environment which has an influence on the behavior
of the plant is the physico-chemical composition of
the soils (Sant' Anna, 1980).
Sudberg (2005) established that β-sitosterol is the
most significant sterol chemical compound which
exists in the extract of P. africana. It can be used as a
marker for the control of the quality of barks of this
species. Kadu et al., (2012) established that most
chemical components of the bark of P. africana are
correlated between themselves. Environmental
parameters such as temperature, precipitation and
the altitude of the sites are not correlated with the
concentration of the aforesaid components. The
metabolic chart of β-sitosterol (Anonym, 2013) shows
that its empirical formula is C29H50 O and developed:
In a natural environment, plants are nourished, from
organic matter transformed beforehand into minerals
by the organisms present in the soils (Larouche,
1983). These soils minerals influence the aspect of
some phonotypic characters of the trees within its
ecosystem.
Materiels and methods
Zone of study
The zones of study (fig. 3) were targeted in two
administrative areas named the South-West and the
North-West Regions of Cameroon, country of Central
Africa.
The choice of these two areas is justified by the
presence of natural regeneration and plantations of P.
africana. In the South-West, the phytogenetic
samples of materials and soils were taken in the Fako
Division whose soils are ferralitic red. In the North-
West, sample selection was made in the Mezam
Division where soils are of the humid cambisol type
(Valerie, 1968).
Experimental field works
The tools used for data collection on the field
consisted of a GPS of GARMINT 5 mark used to
record various altitudes, a numerical camera of mark
HP Photosmart E 427, a digital meter of 7.5 m for
appreciating the circumference of the stem, plastic
bags for pocketing in a separate way the various
samples and a cutlass to carve out the selected
samples of bark and dig out soils.
The geographical co-ordinates of the sampled
populations are given (Table 1).
The experimental scheme is made up of nine
populations where nine composite samples of
phytogenetic and ground materials were collected.
The trees which were the subject of taking away of
bark were beforehand identified with focus on those
with ages varying between 19 and 22 years. Barking
took place under a rainy weather. Each sample of
bark (fig. 4) is removed on the stem, at the height of
1.30 m from the ground and on the face of the stem
exposed to the rays of the sun after midday.
Extraction and isolation of β-sitosterol
The chemical analyses related to the extraction and
isolation of β-sitosterol was carried out in
laboratories. The protocol related to the matter is
given (fig. 5).
The mechanical stages of the analysis related to the
composite bark of each population concerned the
splitting with the cutlass in bits of approximately 5 cm
x 5 cm. The bits are dried on cemented ground or
tarpaulin in the ambient air whose temperature varies
between 25 with 27° C, for seven days. The dried bits
are crushed for obtaining vegetable powder.
The stages of chemical handling related to steeping of
the powder and to filtering it using a special filter
paper. The various parameters of the rotary
evaporator are regulated for obtaining the organic
extracts of nine samples with ethyl-acetate (Fig.6).
Before the isolation of the β-sitosterol, two processes
Tchouakionie et al. Page 4
are used to be sure of the presence of this component
in the bark of P. africana:
The Thin Layer Chromatography which is a physical
technique of separation of chemical species. The
samples resulting from the extracts with the ethyl-
acetate are placed horizontally and on the same level
on paper with a thin layer. Each sample containing
one or more species is moved through a mobile
current phase along the stationary phase constituted
of polar paper with silica. The chemical species which
migrate and stop at the same height as that of the
standard sample of β-sitosterol informs about the
presence of the aforementioned active matter in the
samples under study;
The High Performance Liquid Chromatography
(HPLC) with UV detection wave length at 272 nm was
used for the isolation and qualification of β-sitosterol
of the barks of P. africana.
The quantification of the compound was achieved by
GC-MS through comparing the chromatographic and
spectroscopic data with an authentic standard.
Samples of soils analyses
Concerning edaphic matters, nine composite samples
of soils are obtained from 27 single samples collected
under P. africana trees. Laboratory analyses were
focused on seven characteristics of soils fertility.
Statistical data analyses
The statistical data treated with SAS software was
focused on chi-square test and the factorial
multivariable analyses.
Results and discusion
The effective isolation of β-sitosterol of the barks of P.
africana was carried out in two phases.
The chromatogram obtained from the Thin layer
Chromatography (CCM) is given (Fig. 7).
On the CCM plate, the compounds β-sitosterol of the
various samples of the barks migrated and were
stationed at the same height as that of β-standard
sitosterol. It is thus established that each sample of
bark taken in the area of South-West and the North-
West contains at least some molecules of β-sitostérol.
Table 1. Geo-references of the populations sampled for the barks and soils. NW = North-West, SW = South-
West, PEx = Population of bark x, where x represents the number of the aforementioned population.
N° Populations Longitude Latitude Altitude
(m)
Date of
plantation
Ecosystem or
environment
1 Population PE1
SW/Bova quarter/ Buea
0521604 0451332 885 1992 Agro-forest
plantation
2 Population PE2
SW/Bova quarter/ Buea
0521556 0451141 898 1992 Agro-forest
plantation
3 Population PE3
SW/Kuma-Bokwago /Buea
0521257 0457584 963 1993 Agro-forest
plantation
4 Population PE4
NW/ Majemba quarter/ Bambui
0642243 0661454 1249 1990 Agro-forest
plantation
5 Population PE5
NW/Fely quarter/
Bambui
0642000 0661601 1412 1993 Agro-forest
plantation
6 Population PE6
NW/Atunui quarter/ Bambui
0641448 0661653 1570 1992 Agro-forest
plantation
7 Population PE7
NW/ Water catchment
Bambui
0643760 0666762 1595 1993 Forest of water
catchment
protection
8 Population PE8
NW/ Water catchment
Banbui
0642111 0666516 1596 1993 Forest of water
catchment
protection
9 Population PE9
NW/Akum
0628128 0652407 1639 1992 Agro-forest
plantation
Average 1312 1992 -
Tchouakionie et al. Page 5
The HPLC chromatograms of nine samples of the
extract from the bark of P. africana are produced in
mobile phase and to 50% distilled methanol. The pH
is 6.5 and the ultraviolet detector of rays (UV) was
stabilized to 272 nm. The rays are optimized by
spectrometer using the visible ultraviolet rays. The
temperature is of 25°C and the volume of solvent
injected into the HPLC system is 20 µl. The retention
time for separating β-sitosterol of the barks of various
populations is that which is closest to standard (fig.
8a.), which is 15.501 min. The chromatograms
obtained (fig. 8b) show that, in general at least, the
chemical compound of β-sitosterol exists in all the
samples of barks of P. afrucana collected in the areas
of the South-West and North-West. The
superposition of nine chromatograms of the extract of
the barks from the various sites shows an inking
between those of the AE1, AE3, AE4, AE5, AE6, AE7
and AE8 whereas AE2 and AE9 resemble each other
but present a light difference with the seven others.
These qualitative analyses made it possible to be sure
of the presence of β-sitosterol in the samples of the
barks of P. africana. However, the precision on the
concentration of the aforesaid chemical compound
remains to be determined.
Table 2. Concentration of β-sitosterol in the barks of P. africana PEx = Population of bark x, where x represents
the number of the aforementioned population.
Populations PE1 PE2 PE3 PE4 PE5 PE6 PE7 PE8 PE9
Concentration of β-
sitosterol (µg/ml)
0.00 0.00 14.95 38.65 12.23 15.35 0.00 6.61 18.15
Table 3. Concentration of Lupéol in the barks of P. african PEx = Population of bark x, where x represents the
number of the aforementioned population.
Populations PE1 PE2 PE3 PE4 PE5 PE6 PE7 PE8 PE9
Concentration of
Lupéol (µg/ml)
0.73 0.67 0.28 10.52 0.21 0.49 0.77 0.38 0.17
Gas Chromatography coupled with Mass
Spectrometry (GC-MS) gave the result of the
quantitative analyses of β-sitosterol of the samples of
the barks of the populations of P. africana. The
appreciation of the concentration of β-sitosterol in the
barks of P. africana according to altitude is given
(Fig.9).
Table 4. Correlation between the concentration of β-sitosterol of P. africana and the characteristics of the soils.
Chemical characteristics of the soils Coefficient of correlation with the
concentration of β-sitosterol
Organic matter Total Organic matter (%) 0.01
Organic carbon (%) -0.45
Total Nitrogen (%) -0.42
C/N (%) -0.43
Acid phosphoric-Bray II Assimilable phosphorus (mg/kg) -0.08
Exchange acidity Al3+ + H+ (cmole/kg) -0.53
Exchangeable bases Ca²+ (cmole/kg) -0.40
Mg²+ (cmole/kg) -0.78
K+ (cmole/kg) -0.59
Na+ (cmole/kg) -0.14
S (cmole/kg) -0.77
T(CEC) (cmole/kg) -0.71
V=S/T (100) (cmole/kg) -0.55
Acid / Alkalinity pH.eau-1/2,5 0.14
pH.KCl- 1/2,5 -0.28
Tchouakionie et al. Page 6
From Fig.9, it is established that:
In the population PE1, located at 885 m of altitude in
the South-West area, the content of β-sitosterol is of
zero µg/ml in the sampled barks. The concentration
of β-sitosterol is also zero µg/ml in the barks of
population PE2 located at 898 m of altitude in the
South-West. This result shows that on the site of
mount Cameroon, there are barks of P. africana
which have excessively weak or even null
concentrations of β-sitosterol.
Fig. 1. Various parts for the summary identification
of the adult P. africana’s tree in situ. (A) Adult tree,
(B) Base of trunk and section of bark, (C) Leaves and
fruits.
In population PE3 located at 963 m of altitude on the
mount Cameroon area, the concentration of β-
sitosterol in barks of P. africanais is 14.95 µg/ml. It is
released from this result that the concentration of β-
sitosterol increases as altitude increases compared to
the site of population PE1.
Fig. 2. Genetic bonds in P. africana (Dawson and
Powell, 1999).
The barks of P. africana of the population PE4 at
1249 m of altitude have the biggest concentration of
β-sitosterol, which is 38.65 µg/ml. This result
establishes that the concentration of this active
matter varies according to altitude. The optimum
concentration of β-sitostérol is reached around 1249
m of altitude and beyond this point, the concentration
starts to decrease;
Fig. 3. Zone of study.
The barks of the population PE5 at 1412 m of altitude
at Fely quarter in Bambui in the North-West Region,
have a rate of 12.23 µg/ml. This concentration is in
decrease compared to that of altitudes below 1412 m.
This result shows that after the site of optimum
concentration, β-sitosterol rates drop as one
continues to go up in altitude.
Fig. 4. Cutting out of P. africana’s bark sample
within population PE1.
At 1570 m of altitude where the population PE6 is
found in Majamba quarter, within the peripheral zone
of the Bambui town, β-sitosterol concentration is
15.35 µg/ml. This rate remains weak compared to the
one of this active matter in the barks collected on the
site with maximum concentration. The tendency of
the decrease of β-sitosterol rate as one moves up in
altitude after 1240 m is confirmed.
In the population PE7 located at 1595 m of altitude, in
a forest plantation created for the protection of a
drinking water source locally called " Bambui Water
catchment", the rate of β-sitosterol falls down to zero
µg/ml.
Tchouakionie et al. Page 7
Fig. 5. General protocol of qualitative and
quantitative analyses of β-sitosterol of P. africana.
AEx = Extract with ethyl-acetate from bark x, where x
represents the number of population, CCM = Thin
layer Chromatography, HPLC=High Performance
Liquid Chromatography and GC-MS = Gas
Chromatography coupled with Mass Spectrometry.
At 1596 m of altitude where the population PE8 is
located, still in another portion of the Water
catchment’s forest, the rate of β-sitosterol is 6.61
µg/ml. In spite of a light rise, the aforementioned
content remains very weak compared to that of the
optimum point:
The concentration of β-sitosterol of 18.15 µg/ml of the
population PE9 is found at 1639 m of altitude in the
Bamenda Highland forest. This concentration is high
compared to that of the preceding site.
In general, the concentration of β-sitosterol of the
nine composite samples of P. africana’s barks is given
(Table 2).
To consolidate this result which shows that the
content of β-sitosterol in the bark of P. africana
varies according to the altitude of the forest
plantation site, the quantitative analyses of Lupeol,
generally correlated with the aforementioned active
matter were carried out on the same samples. The
results of the analyses made from the GC-MS is given
(Tableau 3).
The optimum of the rate of Lupéol in the barks of P.
africana is also at 1249 m of altitude in population
PE4 like that of β-sitosterol. This second result
confirms that the rate of β-sitostιrol in the barks of P.
afrcana varies according to altitude.
Fig. 6. Organic extracts of the nine samples with
ethyl-acetate (AE).
The quantitative analysis carried out with GC-MS
establish the absence of β-sitostιrol in the samples of
the barks of populations PE1, PE2 and PE7.
Fig. 7. CCM profile of nine samples of population’s
bark of P. africana. S = β-standard sitosterol, 1 = AE1,
2 = AE2, 3 = AE3, 4 = AE5, 5 = AE6, 7 = AE7, 8 =
AE8, 9 = AE9 and AEx = Extracted with ethyl-acetate
of bark x, where x represents it’s number of the
population.
The result of the analyses of the composites of soil
samples taken under the stems of P. africana and
bearing on 16 X 9 equivalents to 144 physic or
chemical characters is obtained.
Statistical analyses carried out using SAS software
were obtained. ANOVA analyses allowed for
establishing that there is variability with respect to
altitude between the averages of the concentrations of
β-sitosterol of bark of P. africana throughout the
populations; but the differences are not significant.
The chi-square test confirms that locally, there is a
very weak and non-significant correlation (r = 0.17)
between the concentration of β-sitosterol of the bark
Tchouakionie et al. Page 8
of P. africana and the environmental parameter
which is altitude.
Fig. 8a. HPLC Chromatogram of the standard β-
sitosterol.
The regrouping of the populations of P. africana
sampled according to their concentration in β-
sitosterol is carried out. The Analysis in Principal
Components (PCA) targeted on the Ascending
Hierarchical Clustering (CAH) was used for the data
processing. The dendrogram resulting from the CAH
is given (Fig. 10).
Fig. 8b. HPLC Chromatograms of nine samples of
the P. africana’s bark extract. PEx = Population of
bark x, where x represents the number of the
aforementioned population.
The aforementioned dendrogram shows overall three
groups of P. africana’s populations according to the
rate of β-sitosterol of their barks.
The first group is made up of the stems of populations
PE1, PE2, PE7 and PE8. The first two sites of this
group are along the mount Cameroon in the South-
West Region. The populations PE7 and PE8 are in the
North-West Region. The barks sampled in these
populations have the characteristic that their
phenotypic characters materialized by the rate of β-
sitosterol lies between zero and 6.61 µg/ml. The
second group relates to populations PE3, PE5, PE6
and PE9. The barks of the tree of this group have a
rate of β-sitosterol which varies from 12.23 to 14.95
µg/ml. The population PE3 is on the side of mount
Cameroon whereas the other populations of this
group, in particular PE5, PE6 and PE9 are in the area
of the North-West. The third group consists of the
population PE4. The barks of the forest present the
strongest concentration of β-sitosterol which is 38.65
µg/ml. This site is in Bambui in the area of the North-
West.
Fig. 9. Variation of the concentration of β-sitosterol
of P. africana with respect to altitude. PEx =
Population of bark x, where x represents the number
of the aforementioned population.
In accordance with the regrouping resulting from the
CAH, it is established that the best seed-bearing ones
with respect to β-sitosterol concentration are in the
populations of group II and III.
Correlation between the rate of β-sitosterol of P.
africana and the chemical characteristics of the soils
is given (Table 4.).
Fig. 10. Dendrogram resulting from the CAH of the
concentration of β-sitosterol in the bark of P.
africana.
The table shows 15 coefficients of correlation between
the chemical characteristics of the soils and the
concentration of β-sitosterol of P. africana. With the
exception of two coefficients, particularly that
between the total organic matter (r = 0.01) as well as
pH KCL (r = 0.14) and the content of β-sitosterol
Tchouakionie et al. Page 9
which are positive but non-significant, the thirteen
others which vary from -0.78 to -0.14 are negative
and non-significant. It is thus established that in the
natural environment, there is no relevant correlation
between the chemical elements of the soils and the
concentration of β–sitosterol. The phenotypic
character materialized by the concentration of β-
sitosterol of P. Africana is thus influenced much more
by genetic parameters than environmental factors. In
other words, the abiotic factors have a weak influence
on the content of β-sitosterol of this forest species.
Discussion
Contrary to the results of Sudberg, (2005) who found
a concentration in β-sitosterol from 29.10 to 32.43
µg/ml in three samples of the bark of P. africana, the
present study highlights that rate of β-sitosterol in the
extract of the bark of P. africana varies from zero (0)
to 38,65 µg/ml. This result is relevant as the barks
collected on the stems of populations PE1, PE2 and
PE7 do not contain β-sitosterol and cannot
consequently give the satisfaction discounted within
the framework of phytotherapy. The genetic bond can
justify the bringing together of populations PE1 and
PE2 having a rate of zero in a site in the South-West
and population PE7 in the North-West area. The
seeds which were used with the installation of the
above-mentioned populations can result from the
same source. This study confirms the result of Kadu
et al., (2012) which established that the
environmental parameters are not generally
correlated with the concentration of the chemical
components of bark of P. africana. It even adds that
the chemical elements of the soils have a very weak
influence on the concentration of β-sitosterol of P.
africana. Pilate (2002) establishes that for forest
trees, characters targeted for selection such as the
volume of the barrel or the density of wood are
strongly or fairly influenced by the environment. This
means that they are less heritable; but the
concentration of β-sitosterol could rather be a
phenotypic character with heritable prevalence.
Conclusion
The qualitative analyses of β-sitosterol of barks of P.
africana shows the presence at least in trace of this
bioactive constituent in all samples of the plants
collected in the areas of the South-West and the
North-West of Cameroon. The quantitative analyses
however establish that the populations of P. africana,
PE1, PE2 and PE7 have barks which do not contain
the β-sitosterol. This result is relevant because the
barks collected within the above-mentioned
populations cannot give the satisfaction discounted
within the framework of phytotherapy. Locally, there
is no significant correlation between the
concentration of β-sitosterol of barks of P. africana
and the environmental parameter which is altitude.
The CAH set out the populations in three groups. The
first group is made up of the stems of populations
PE1, PE2, PE7 and PE8. The phenotypic character
materialized by the concentration of β-sitosterol of
this group varies from zero to 6.61 µg/ml. The second
group relates to populations PE3, PE5, PE6 and PE9.
The rate of β-sitosterol of the tree barks of this group
varies from 12.23 to 14.95 µg/ml. The third group is
made up of the population PE4 whose concentration
of β-sitosterol reaches 38.65 µg/ml.
There is no relevant correlation between the chemical
elements of the soils and the concentration of β-
sitosterol of P. africana. Consequently, the
aforementioned phenotypic character is influenced
much more by genetic parameters than
environmental factors.
The tools thus obtained are essential for the
management of the ground and the exploited
products of this species, as well as the production of
the seeds for the installation of forest and agro-forest
plantations.
In prospect, the creation of the plantations of P.
africana starting from seeds coming from the stems
of populations PE1, PE2 or PE7 could lead to the
establishment of forest trees whose barks do not have
the principal bioactive matter, characteristic of this
medicinal plant. In the short term, it will be advisable
to carry out the sensitizing of the peasants and public
authority for the collection of the seeds preferably
Tchouakionie et al. Page 10
within the populations of the second and third group.
On the long run, it is necessary to carry out a research
on the production of seeds by in vitro culture whose
explants will come from better stems of populations
PE3, PE4, PE5, PE6 and PE9 and thus, improve the
current practice of sylviculture in Cameroon.
Acknowledgements
We present our gratitude to the Center of
Environmental and Social Management (CEGES),
with the members of the scientific teams of the
Laboratory of Plant Biotechnology and Environment
of the University of Yaounde I and those of the
Laboratory of the Natural Substances of the Higher
Teachers’ Training College (ENS) of Yaounde all in
Cameroon, as well as the Institute of Environmental
Research (INFU), Department of Chemistry and
Biology, Chair of Environmental Chemistry and
Analytical Chemistry in Germany, for their multiform
contributions.
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Effect of some abiotic factors on the concentration of β- sitosterol of Prunus Africana (Hook.f.) Kalkman in the tropical forests of Cameroon

  • 1. Tchouakionie et al. Page 1 RESEARCH PAPER OPEN ACCESS Effect of some abiotic factors on the concentration of β- sitosterol of Prunus Africana (Hook.f.) Kalkman in the tropical forests of Cameroon Maurice Tchouakionie1* , Emmanuel Youmbi2 , Michel Ndoumbe Nkeng3 , Siméon Fogue Kouam4 , Marc Lamshôft5 , Michael Spiteller5 1 Laboratory of Plant Biotechnology and Environment, Department of Plant Biology, Faculty of Science, University of Yaounde I, P.O. Box: 812 Yaounde, Cameroon 2 Department of Plant Biology, Faculty of Science, University of Yaounde I, P.O. Box: 812 Yaounde. Cameroon 3 Institute of Agricultural Research for Development (IRAD) Yaounde. P.O. Box: 2123 Yaounde, 4 Department of Chemistry, Higher Teachers’ Training College, University of Yaounde 1, P.O. Box 47 Yaounde, Cameroon 5 Institute of Environmental Research (INFU), Department of Chemistry and Biology, Chair of Environmental Chemistry and Analytical Chemistry, TU Dortmund Otto-Haln-Sir 6 D-14221 Dortmund, Germany Article published on February 25, 2014 Key words: Prunus africana, phenotypic character, soils, β-sitosterol, altitude. Abstract Prunus africana is a medicinal plant which develops in the mountains of several African countries. β-sitosterol can be used as a marker for the control of the product quality of the aforementioned plant in terms of phytotherapy. Farmers and public authorities do not have information on the influence of altitude and chemical characteristics of soils on the concentration of β- sitosterol of P. africana. To contribute to solve the problem, this research, carried out in Cameroon, aims to appreciate the effect of abiotic factors on the above phenotypic character. In nine composite samples of barks taken at different altitudes, the concentration of β-sitosterol is appreciated via qualitative analyses by Thin Layer Chromatography, High Performance Liquid Chromatography and quantitative analyses by Gas Chromatography coupled with the Mass Spectrometry. The chemical analyses of soils taken under the stems of the aforementioned trees were made. The statistics were carried out using the SAS software. The concentration of β-sitosterol in each population of P. africana varies from zero to 38.65 µg/ml. There is variability between the averages of the aforementioned concentration with respect to altitude and chemical elements of the soils but the differences are not significant. The Ascending Hierarchical Clustering distributes populations into three groups. These tools obtained are indispensable for the ground management, the products exploited from this tree species and the production of seeds for creating forest and agro-forest plantations. * Corresponding Author: Maurice Tchouakionie  tchouakionie@yahoo.fr International Journal of Agronomy and Agricultural Research (IJAAR) ISSN: 2223-7054 (Print) 2225-3610 (Online) http://www.innspub.net Vol. 4, No. 2, p. 1-11, 2014
  • 2. Tchouakionie et al. Page 2 Introduction Prunus africana (Hook. F.) Kalkman is a medicinal plant which develops in the forests of mountains at altitudes going from 700 m to more than 1000 m in several countries of Africa (Avery et al., 2001). Its bark is exploited and marketed internationally because of its effectiveness in the treatment of benign prostates and hyperplasia (Watt and Bryer, 1962, Bankill, 1997, cit. by Hall et al., 2000). In pecuniary terms of value, one Kilogram of rough bark is bought at 300 F CFA from farmers and the drawn extract from the aforesaid Kilogram costs 500 000 F. CFA in pharmaceutical industries (Vockins, 2000, cit. Avana et al., 2006). P. africana is a component of biodiversity which represents 6 % of the species used for forest and agro- forest plantations in the agro-ecological zone of the high plateaus of the West of Cameroon (Tchouakionie et al, 2010). To optimize the output of the plantations, it is necessary to take into account the biotic and abiotic factors relating to the P. africana. The small farmers and public authorities do not have formal information on the variability of the concentration of β-sitosterol, the principal active matter of P. africana with respect to altitude and the chemical characteristics of the soils of the aforementioned species plantations. The general objective of this study is to appreciate the effect of some abiotic factors on the concentration of β-sitosterol of P. africana within mount Cameroon and the Bamenda high land areas. To achieve this goal, three specific objectives were formulated: To evaluate the effect of altitude on the concentration of β-sitosterol of P. africana; to appreciate the correlation between the chemical characteristics of the soils and the concentration of β-sitosterol of the aforementioned species; to group the populations of P. africana according to their concentration in β-sitosterol. In the biological context, P. africana belongs to the family of Rosaceae and are found practically only on mountains (Letouzey, 1982).The detailed description of the adult tree is materialized by characteristic phytogenetic parts (fig. 1). The stem (Fig.1.A) is a seed-bearer in an agro- ecosystem in Akum, within Mezam Division, in the North-West of Cameroon. The base of trunk presents a simple footing of 8-10 cm (Fig.1. B). The young seedlings are visible under this tree. These seedlings come from two modes of pollination in particular: self-fertilization and cross-pollinated parents. Pollination here is primarily entomophilous. However the implication of certain birds was noted (Avana, 2006). Flowering is irregular in P. africana and occurs every 2 to 3 years. Fructification intervenes 2 to 3 months after the beginning of flowering. The number of fruits per inflorescence varies from 1 to 6 units (Fig. 1.C). The natural ecological zone of P. africana in Cameroon is confined to the mountain and sub- mountain forests of altitudes ranging between 1500- 3000 m (Vivien and Faure, 2011). The surface distribution of the forests of P. africana planted from 1976 to 2007, reached 625 ha with at least 1.526.430 trees (Kadu et al., 2012). The peasants partly receive seeds from non-governmental organizations and official establishments. Concerning the influence of biotic factors on the development of P. africana, analyses carried out by Dawson and Powell (1999) using molecular markers indicated that the variation is quite effective at the level of the genes (fig. 2). There are quantitative and qualitative differences in chemical compounds from the barks of P. africana within geographically dispersed populations (Hall et al., 2000). The concentration of β-sitosterol, the major component of the bark of P. africana, varies from 101 to 150 µg/ml between origins and 50 to 191µg/ml between individuals (Simons and Leakey, 2004, cit. Avana, 2006). One of the factors of the
  • 3. Tchouakionie et al. Page 3 environment which has an influence on the behavior of the plant is the physico-chemical composition of the soils (Sant' Anna, 1980). Sudberg (2005) established that β-sitosterol is the most significant sterol chemical compound which exists in the extract of P. africana. It can be used as a marker for the control of the quality of barks of this species. Kadu et al., (2012) established that most chemical components of the bark of P. africana are correlated between themselves. Environmental parameters such as temperature, precipitation and the altitude of the sites are not correlated with the concentration of the aforesaid components. The metabolic chart of β-sitosterol (Anonym, 2013) shows that its empirical formula is C29H50 O and developed: In a natural environment, plants are nourished, from organic matter transformed beforehand into minerals by the organisms present in the soils (Larouche, 1983). These soils minerals influence the aspect of some phonotypic characters of the trees within its ecosystem. Materiels and methods Zone of study The zones of study (fig. 3) were targeted in two administrative areas named the South-West and the North-West Regions of Cameroon, country of Central Africa. The choice of these two areas is justified by the presence of natural regeneration and plantations of P. africana. In the South-West, the phytogenetic samples of materials and soils were taken in the Fako Division whose soils are ferralitic red. In the North- West, sample selection was made in the Mezam Division where soils are of the humid cambisol type (Valerie, 1968). Experimental field works The tools used for data collection on the field consisted of a GPS of GARMINT 5 mark used to record various altitudes, a numerical camera of mark HP Photosmart E 427, a digital meter of 7.5 m for appreciating the circumference of the stem, plastic bags for pocketing in a separate way the various samples and a cutlass to carve out the selected samples of bark and dig out soils. The geographical co-ordinates of the sampled populations are given (Table 1). The experimental scheme is made up of nine populations where nine composite samples of phytogenetic and ground materials were collected. The trees which were the subject of taking away of bark were beforehand identified with focus on those with ages varying between 19 and 22 years. Barking took place under a rainy weather. Each sample of bark (fig. 4) is removed on the stem, at the height of 1.30 m from the ground and on the face of the stem exposed to the rays of the sun after midday. Extraction and isolation of β-sitosterol The chemical analyses related to the extraction and isolation of β-sitosterol was carried out in laboratories. The protocol related to the matter is given (fig. 5). The mechanical stages of the analysis related to the composite bark of each population concerned the splitting with the cutlass in bits of approximately 5 cm x 5 cm. The bits are dried on cemented ground or tarpaulin in the ambient air whose temperature varies between 25 with 27° C, for seven days. The dried bits are crushed for obtaining vegetable powder. The stages of chemical handling related to steeping of the powder and to filtering it using a special filter paper. The various parameters of the rotary evaporator are regulated for obtaining the organic extracts of nine samples with ethyl-acetate (Fig.6). Before the isolation of the β-sitosterol, two processes
  • 4. Tchouakionie et al. Page 4 are used to be sure of the presence of this component in the bark of P. africana: The Thin Layer Chromatography which is a physical technique of separation of chemical species. The samples resulting from the extracts with the ethyl- acetate are placed horizontally and on the same level on paper with a thin layer. Each sample containing one or more species is moved through a mobile current phase along the stationary phase constituted of polar paper with silica. The chemical species which migrate and stop at the same height as that of the standard sample of β-sitosterol informs about the presence of the aforementioned active matter in the samples under study; The High Performance Liquid Chromatography (HPLC) with UV detection wave length at 272 nm was used for the isolation and qualification of β-sitosterol of the barks of P. africana. The quantification of the compound was achieved by GC-MS through comparing the chromatographic and spectroscopic data with an authentic standard. Samples of soils analyses Concerning edaphic matters, nine composite samples of soils are obtained from 27 single samples collected under P. africana trees. Laboratory analyses were focused on seven characteristics of soils fertility. Statistical data analyses The statistical data treated with SAS software was focused on chi-square test and the factorial multivariable analyses. Results and discusion The effective isolation of β-sitosterol of the barks of P. africana was carried out in two phases. The chromatogram obtained from the Thin layer Chromatography (CCM) is given (Fig. 7). On the CCM plate, the compounds β-sitosterol of the various samples of the barks migrated and were stationed at the same height as that of β-standard sitosterol. It is thus established that each sample of bark taken in the area of South-West and the North- West contains at least some molecules of β-sitostérol. Table 1. Geo-references of the populations sampled for the barks and soils. NW = North-West, SW = South- West, PEx = Population of bark x, where x represents the number of the aforementioned population. N° Populations Longitude Latitude Altitude (m) Date of plantation Ecosystem or environment 1 Population PE1 SW/Bova quarter/ Buea 0521604 0451332 885 1992 Agro-forest plantation 2 Population PE2 SW/Bova quarter/ Buea 0521556 0451141 898 1992 Agro-forest plantation 3 Population PE3 SW/Kuma-Bokwago /Buea 0521257 0457584 963 1993 Agro-forest plantation 4 Population PE4 NW/ Majemba quarter/ Bambui 0642243 0661454 1249 1990 Agro-forest plantation 5 Population PE5 NW/Fely quarter/ Bambui 0642000 0661601 1412 1993 Agro-forest plantation 6 Population PE6 NW/Atunui quarter/ Bambui 0641448 0661653 1570 1992 Agro-forest plantation 7 Population PE7 NW/ Water catchment Bambui 0643760 0666762 1595 1993 Forest of water catchment protection 8 Population PE8 NW/ Water catchment Banbui 0642111 0666516 1596 1993 Forest of water catchment protection 9 Population PE9 NW/Akum 0628128 0652407 1639 1992 Agro-forest plantation Average 1312 1992 -
  • 5. Tchouakionie et al. Page 5 The HPLC chromatograms of nine samples of the extract from the bark of P. africana are produced in mobile phase and to 50% distilled methanol. The pH is 6.5 and the ultraviolet detector of rays (UV) was stabilized to 272 nm. The rays are optimized by spectrometer using the visible ultraviolet rays. The temperature is of 25°C and the volume of solvent injected into the HPLC system is 20 µl. The retention time for separating β-sitosterol of the barks of various populations is that which is closest to standard (fig. 8a.), which is 15.501 min. The chromatograms obtained (fig. 8b) show that, in general at least, the chemical compound of β-sitosterol exists in all the samples of barks of P. afrucana collected in the areas of the South-West and North-West. The superposition of nine chromatograms of the extract of the barks from the various sites shows an inking between those of the AE1, AE3, AE4, AE5, AE6, AE7 and AE8 whereas AE2 and AE9 resemble each other but present a light difference with the seven others. These qualitative analyses made it possible to be sure of the presence of β-sitosterol in the samples of the barks of P. africana. However, the precision on the concentration of the aforesaid chemical compound remains to be determined. Table 2. Concentration of β-sitosterol in the barks of P. africana PEx = Population of bark x, where x represents the number of the aforementioned population. Populations PE1 PE2 PE3 PE4 PE5 PE6 PE7 PE8 PE9 Concentration of β- sitosterol (µg/ml) 0.00 0.00 14.95 38.65 12.23 15.35 0.00 6.61 18.15 Table 3. Concentration of Lupéol in the barks of P. african PEx = Population of bark x, where x represents the number of the aforementioned population. Populations PE1 PE2 PE3 PE4 PE5 PE6 PE7 PE8 PE9 Concentration of Lupéol (µg/ml) 0.73 0.67 0.28 10.52 0.21 0.49 0.77 0.38 0.17 Gas Chromatography coupled with Mass Spectrometry (GC-MS) gave the result of the quantitative analyses of β-sitosterol of the samples of the barks of the populations of P. africana. The appreciation of the concentration of β-sitosterol in the barks of P. africana according to altitude is given (Fig.9). Table 4. Correlation between the concentration of β-sitosterol of P. africana and the characteristics of the soils. Chemical characteristics of the soils Coefficient of correlation with the concentration of β-sitosterol Organic matter Total Organic matter (%) 0.01 Organic carbon (%) -0.45 Total Nitrogen (%) -0.42 C/N (%) -0.43 Acid phosphoric-Bray II Assimilable phosphorus (mg/kg) -0.08 Exchange acidity Al3+ + H+ (cmole/kg) -0.53 Exchangeable bases Ca²+ (cmole/kg) -0.40 Mg²+ (cmole/kg) -0.78 K+ (cmole/kg) -0.59 Na+ (cmole/kg) -0.14 S (cmole/kg) -0.77 T(CEC) (cmole/kg) -0.71 V=S/T (100) (cmole/kg) -0.55 Acid / Alkalinity pH.eau-1/2,5 0.14 pH.KCl- 1/2,5 -0.28
  • 6. Tchouakionie et al. Page 6 From Fig.9, it is established that: In the population PE1, located at 885 m of altitude in the South-West area, the content of β-sitosterol is of zero µg/ml in the sampled barks. The concentration of β-sitosterol is also zero µg/ml in the barks of population PE2 located at 898 m of altitude in the South-West. This result shows that on the site of mount Cameroon, there are barks of P. africana which have excessively weak or even null concentrations of β-sitosterol. Fig. 1. Various parts for the summary identification of the adult P. africana’s tree in situ. (A) Adult tree, (B) Base of trunk and section of bark, (C) Leaves and fruits. In population PE3 located at 963 m of altitude on the mount Cameroon area, the concentration of β- sitosterol in barks of P. africanais is 14.95 µg/ml. It is released from this result that the concentration of β- sitosterol increases as altitude increases compared to the site of population PE1. Fig. 2. Genetic bonds in P. africana (Dawson and Powell, 1999). The barks of P. africana of the population PE4 at 1249 m of altitude have the biggest concentration of β-sitosterol, which is 38.65 µg/ml. This result establishes that the concentration of this active matter varies according to altitude. The optimum concentration of β-sitostérol is reached around 1249 m of altitude and beyond this point, the concentration starts to decrease; Fig. 3. Zone of study. The barks of the population PE5 at 1412 m of altitude at Fely quarter in Bambui in the North-West Region, have a rate of 12.23 µg/ml. This concentration is in decrease compared to that of altitudes below 1412 m. This result shows that after the site of optimum concentration, β-sitosterol rates drop as one continues to go up in altitude. Fig. 4. Cutting out of P. africana’s bark sample within population PE1. At 1570 m of altitude where the population PE6 is found in Majamba quarter, within the peripheral zone of the Bambui town, β-sitosterol concentration is 15.35 µg/ml. This rate remains weak compared to the one of this active matter in the barks collected on the site with maximum concentration. The tendency of the decrease of β-sitosterol rate as one moves up in altitude after 1240 m is confirmed. In the population PE7 located at 1595 m of altitude, in a forest plantation created for the protection of a drinking water source locally called " Bambui Water catchment", the rate of β-sitosterol falls down to zero µg/ml.
  • 7. Tchouakionie et al. Page 7 Fig. 5. General protocol of qualitative and quantitative analyses of β-sitosterol of P. africana. AEx = Extract with ethyl-acetate from bark x, where x represents the number of population, CCM = Thin layer Chromatography, HPLC=High Performance Liquid Chromatography and GC-MS = Gas Chromatography coupled with Mass Spectrometry. At 1596 m of altitude where the population PE8 is located, still in another portion of the Water catchment’s forest, the rate of β-sitosterol is 6.61 µg/ml. In spite of a light rise, the aforementioned content remains very weak compared to that of the optimum point: The concentration of β-sitosterol of 18.15 µg/ml of the population PE9 is found at 1639 m of altitude in the Bamenda Highland forest. This concentration is high compared to that of the preceding site. In general, the concentration of β-sitosterol of the nine composite samples of P. africana’s barks is given (Table 2). To consolidate this result which shows that the content of β-sitosterol in the bark of P. africana varies according to the altitude of the forest plantation site, the quantitative analyses of Lupeol, generally correlated with the aforementioned active matter were carried out on the same samples. The results of the analyses made from the GC-MS is given (Tableau 3). The optimum of the rate of Lupéol in the barks of P. africana is also at 1249 m of altitude in population PE4 like that of β-sitosterol. This second result confirms that the rate of β-sitostιrol in the barks of P. afrcana varies according to altitude. Fig. 6. Organic extracts of the nine samples with ethyl-acetate (AE). The quantitative analysis carried out with GC-MS establish the absence of β-sitostιrol in the samples of the barks of populations PE1, PE2 and PE7. Fig. 7. CCM profile of nine samples of population’s bark of P. africana. S = β-standard sitosterol, 1 = AE1, 2 = AE2, 3 = AE3, 4 = AE5, 5 = AE6, 7 = AE7, 8 = AE8, 9 = AE9 and AEx = Extracted with ethyl-acetate of bark x, where x represents it’s number of the population. The result of the analyses of the composites of soil samples taken under the stems of P. africana and bearing on 16 X 9 equivalents to 144 physic or chemical characters is obtained. Statistical analyses carried out using SAS software were obtained. ANOVA analyses allowed for establishing that there is variability with respect to altitude between the averages of the concentrations of β-sitosterol of bark of P. africana throughout the populations; but the differences are not significant. The chi-square test confirms that locally, there is a very weak and non-significant correlation (r = 0.17) between the concentration of β-sitosterol of the bark
  • 8. Tchouakionie et al. Page 8 of P. africana and the environmental parameter which is altitude. Fig. 8a. HPLC Chromatogram of the standard β- sitosterol. The regrouping of the populations of P. africana sampled according to their concentration in β- sitosterol is carried out. The Analysis in Principal Components (PCA) targeted on the Ascending Hierarchical Clustering (CAH) was used for the data processing. The dendrogram resulting from the CAH is given (Fig. 10). Fig. 8b. HPLC Chromatograms of nine samples of the P. africana’s bark extract. PEx = Population of bark x, where x represents the number of the aforementioned population. The aforementioned dendrogram shows overall three groups of P. africana’s populations according to the rate of β-sitosterol of their barks. The first group is made up of the stems of populations PE1, PE2, PE7 and PE8. The first two sites of this group are along the mount Cameroon in the South- West Region. The populations PE7 and PE8 are in the North-West Region. The barks sampled in these populations have the characteristic that their phenotypic characters materialized by the rate of β- sitosterol lies between zero and 6.61 µg/ml. The second group relates to populations PE3, PE5, PE6 and PE9. The barks of the tree of this group have a rate of β-sitosterol which varies from 12.23 to 14.95 µg/ml. The population PE3 is on the side of mount Cameroon whereas the other populations of this group, in particular PE5, PE6 and PE9 are in the area of the North-West. The third group consists of the population PE4. The barks of the forest present the strongest concentration of β-sitosterol which is 38.65 µg/ml. This site is in Bambui in the area of the North- West. Fig. 9. Variation of the concentration of β-sitosterol of P. africana with respect to altitude. PEx = Population of bark x, where x represents the number of the aforementioned population. In accordance with the regrouping resulting from the CAH, it is established that the best seed-bearing ones with respect to β-sitosterol concentration are in the populations of group II and III. Correlation between the rate of β-sitosterol of P. africana and the chemical characteristics of the soils is given (Table 4.). Fig. 10. Dendrogram resulting from the CAH of the concentration of β-sitosterol in the bark of P. africana. The table shows 15 coefficients of correlation between the chemical characteristics of the soils and the concentration of β-sitosterol of P. africana. With the exception of two coefficients, particularly that between the total organic matter (r = 0.01) as well as pH KCL (r = 0.14) and the content of β-sitosterol
  • 9. Tchouakionie et al. Page 9 which are positive but non-significant, the thirteen others which vary from -0.78 to -0.14 are negative and non-significant. It is thus established that in the natural environment, there is no relevant correlation between the chemical elements of the soils and the concentration of β–sitosterol. The phenotypic character materialized by the concentration of β- sitosterol of P. Africana is thus influenced much more by genetic parameters than environmental factors. In other words, the abiotic factors have a weak influence on the content of β-sitosterol of this forest species. Discussion Contrary to the results of Sudberg, (2005) who found a concentration in β-sitosterol from 29.10 to 32.43 µg/ml in three samples of the bark of P. africana, the present study highlights that rate of β-sitosterol in the extract of the bark of P. africana varies from zero (0) to 38,65 µg/ml. This result is relevant as the barks collected on the stems of populations PE1, PE2 and PE7 do not contain β-sitosterol and cannot consequently give the satisfaction discounted within the framework of phytotherapy. The genetic bond can justify the bringing together of populations PE1 and PE2 having a rate of zero in a site in the South-West and population PE7 in the North-West area. The seeds which were used with the installation of the above-mentioned populations can result from the same source. This study confirms the result of Kadu et al., (2012) which established that the environmental parameters are not generally correlated with the concentration of the chemical components of bark of P. africana. It even adds that the chemical elements of the soils have a very weak influence on the concentration of β-sitosterol of P. africana. Pilate (2002) establishes that for forest trees, characters targeted for selection such as the volume of the barrel or the density of wood are strongly or fairly influenced by the environment. This means that they are less heritable; but the concentration of β-sitosterol could rather be a phenotypic character with heritable prevalence. Conclusion The qualitative analyses of β-sitosterol of barks of P. africana shows the presence at least in trace of this bioactive constituent in all samples of the plants collected in the areas of the South-West and the North-West of Cameroon. The quantitative analyses however establish that the populations of P. africana, PE1, PE2 and PE7 have barks which do not contain the β-sitosterol. This result is relevant because the barks collected within the above-mentioned populations cannot give the satisfaction discounted within the framework of phytotherapy. Locally, there is no significant correlation between the concentration of β-sitosterol of barks of P. africana and the environmental parameter which is altitude. The CAH set out the populations in three groups. The first group is made up of the stems of populations PE1, PE2, PE7 and PE8. The phenotypic character materialized by the concentration of β-sitosterol of this group varies from zero to 6.61 µg/ml. The second group relates to populations PE3, PE5, PE6 and PE9. The rate of β-sitosterol of the tree barks of this group varies from 12.23 to 14.95 µg/ml. The third group is made up of the population PE4 whose concentration of β-sitosterol reaches 38.65 µg/ml. There is no relevant correlation between the chemical elements of the soils and the concentration of β- sitosterol of P. africana. Consequently, the aforementioned phenotypic character is influenced much more by genetic parameters than environmental factors. The tools thus obtained are essential for the management of the ground and the exploited products of this species, as well as the production of the seeds for the installation of forest and agro-forest plantations. In prospect, the creation of the plantations of P. africana starting from seeds coming from the stems of populations PE1, PE2 or PE7 could lead to the establishment of forest trees whose barks do not have the principal bioactive matter, characteristic of this medicinal plant. In the short term, it will be advisable to carry out the sensitizing of the peasants and public authority for the collection of the seeds preferably
  • 10. Tchouakionie et al. Page 10 within the populations of the second and third group. On the long run, it is necessary to carry out a research on the production of seeds by in vitro culture whose explants will come from better stems of populations PE3, PE4, PE5, PE6 and PE9 and thus, improve the current practice of sylviculture in Cameroon. Acknowledgements We present our gratitude to the Center of Environmental and Social Management (CEGES), with the members of the scientific teams of the Laboratory of Plant Biotechnology and Environment of the University of Yaounde I and those of the Laboratory of the Natural Substances of the Higher Teachers’ Training College (ENS) of Yaounde all in Cameroon, as well as the Institute of Environmental Research (INFU), Department of Chemistry and Biology, Chair of Environmental Chemistry and Analytical Chemistry in Germany, for their multiform contributions. References Anonym. 2013. Showing metabocard for Beta- sitosterol (HMDB00852), Canada.5 p. Avana TML. 2006. Domestication de Prunus africana (Hook, f.) Kalkam (Rosaseae) : Etude de la germination et du bouturage.Thèse de Doctorat (Ph.D), Université de Yaoundé I. 8-115. Avery R, Wirsly E, Etorie M, Ewane D. 2001. Prunus: A Booklet for Extension Workers, Limbe Botanic Garden. 6-21. Dawson IK, Powell W. 1999. Genetic variation in the afromontane tree Prunus africana, an endangered medicinal species. Molecular Ecology, Nairobi. 123-156. Letouzey R. 1982. Manuel de Botanique Forestière Afrique Tropicale, Tome 2A, Centre Technique Forestier Tropical. 169 -170. Hall JB, O'Brien EM, Sinclair FL. 2000. Prunus africana: a monograph. School of Agricultural and Forest Sciences: University of Wales, Publication Number 18, 55 -104. Kadu CA, Parich A, Schueler S, Konrad H, Mulund G.M, Eyog-Hatig O, Muchugi A, Williams VL, Ramamoniisca L, Kapinga C, Foahom B, Katsyanga C,Hafashimana D, Obama C, Vinceli B, Schumacher R, Geburk T. 2012. Bioactive constituents in Prunus africana: geographical variation through out Africa and associations with environmental and genetic parameters, Elsevier, Federal Research Centre for Forests, Department of Forest Genetics, Vienna, Austria. 10 -18. Larouche AR. 1983. La matière organique et ses décomposeurs : l'équipe par. Excellence en jardinage, Projets pour une agriculture écologique. Collège Macdonald, Université McGill, Québec, Canada. 4-10. Pilate G, Pâques M, Leplé JC, Plomion C. 2002. Les biotechnologies chez les arbres forestiers, outils et méthodes : Unité Amélioration, Génétique et Physiologie forestières INRA-Orléans. France. 12-20. Sant'Anna R. 1980. Major soils for food production in Africa, FAO: Natural Resource Management and Environment Department, Rome, Italy. 14-22. Sudberg S. 2005. Optimization of extraction methods of some of the pentacyclictriterpenes, sterols and linear alcohols and quantification of β-sitosterol in Prunus africana (Hook. f.) Kalkman [Rosaceae] by High Performance Thin-Layer Chromatography (HPTLC) with comparative analysis by HPLC, Alkemists Pharmaceuticals, Inc: the plant authentication experts, Florida, USA. 22-33. Tchouakionie M, Youmbi E, Amougou Akoa, NdoumbeNkeng M. 2010. Study of phenotypic characters of Prunus africana (Hook. f.) Kalkman relating to altitudes in two regions of Cameroon, Book of abstracts, Cameroon Biosciences Society (CBS), Yaounde, Cameroon. 49-50.
  • 11. Tchouakionie et al. Page 11 Valérie M. 1968. Notice explicative: carte pédologique du Cameroun Occidental au 1/1000.000, Office de la Recherche Scientifique et Technique Outre-mer (O.R.S.T.O.M), Centre de Yaoundé 165, 69-70. Vivien J, Faure JJ. 2011. Arbres des forêts denses d’Afrique Centrale, COMIFAC, GIZ et la Fondation pour la Tri-National de la Sangha (TNS), Project Resource Management (PRM), Rouen, France. 652- 653.