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Firewood potential production of three sahelian woody species (Grewia bicolor, Pterocarpus lucens and Combretum glutinosum) in Ferlo (northern Senegal).

Introduction

Firewood is the main domestic source of energy in Ferlo. It offers an essential service to local communities. However, very few studies evaluate the firewood production in sahelian context. Indeed, knowledge on the savannas' productivities [4,7,15,12,21] revealed complexity and diversity of the answers to questions addressing productivity [17], particularly regarding the firewood production. Indeed, most of the methods estimating the wood production in savannas miss the heterogeneity of settlements and production targets (sawlog, service wood and firewood). Thus, methods integrating the various productions (sawlog, service and firewood, forages, fruits), diversity and dynamics of the woody formations [6] are needed. This estimation is essential for establishing a precized assessment between needs and resources, particularly regarding the firewood [5]. The present work lists for Ferlo savanna, the mostly used species, establishes predictive models for the wood potential and evaluates the needs and the potentialities of production of the ligneous.

Material And Method

Study area:

The study was undertaken in the rural community of Velingara-Ferlo in northern Senegal (14[degrees]24'-16[degrees]11'NL and 13[degrees]07'-14[degrees]51'W longitude) (figure 1). It is situated between administrative Matam, Louga and Saint-Louis. Three main ethnic groups i.e. Peuls, Wolofs and Moors prevailed with a more dominance of Peuls. Ferlo is established on dune sandy formations of the continental terminal. The landscape is marked with slopes lower than 3% affecting evolution of the mediums and discriminated three main types of soil: sandy soils, a gradient of clayed-sandy to clayed soils and lateritic soils. The climate is sudano-sahelian characterized by a three-month rainy season high thermal amplitude. The maximum temperature reached 40.4[degrees]C in May. The annual average temperature is 28.6[degrees]C while the minimal monthly average temperatures are 14.1[degrees]C in January.

[FIGURE 1 OMITTED]

Precipitations are concentrated in July, August and September. The Ranerou station'rain averaged 474 mm (from 1951 to 2011). Since 1970, more than 25% of the annual rain is lower than the dry inter-annual mean value as these years belong to the driest ones. Chorologically, the biosphere reserve holds both sahelian formations and sudanian savannas. The woody layer is dominated by shrubs with mainly Combretum glutinosum, Pterocarpus lucens, Guiera senegalensis, Grewia bicolor, Acacia Senegal, Balanites aegyptiaca, etc. The herbaceous layer is marked by grass species such as Cenchrus biflorus, Schoenfeldia gracilis, Eragrostis tremula and Dactyloctenium aegyptium.

Method:

This work uses socio-economic and ecological data. Observations, measurements and investigations from women in 40 smallholders provide knowledge and information on the mostly used firewood species and help in estimating the daily consumption of firewood. The plant material for assessing the wood potential consists in Combretum glutinosum, Grewia bicolor and Pterocarpus lucens. Each sampled tree is measured for circumference at the basis and height. Various branches were clustered in three groups namely respectively large, averages and small branches. Branches were sampled per group, crossed, defoliated and weighed (figure 2). Each branch was measured for the length and circumference before the weighing. This method of standards branches helps in building the regression linking the dry matter to the basal circumference per branch and/or to the length of the corresponding branches [13]. Thus, a model expressing an allometric relation of the form:

Y= A x [X.sup.b] with a coefficient of determination ([R.sup.2]) between the variables Y and X.

Y is the woody production in kg ms (P) and X, the circumference in cm (C).

The power b indicates the range of magnitude in Y when X increases [3]. The force of the link between the two variables is estimated by the coefficient of determination [R.sup.2], ranging between 0 and 1. The relationship is strong when [R.sup.2] approaches 1 [9].

The dry matter rate (MS) was obtained after the wood discs samples were oven dried at 105[degrees]C until a constant weight.

The evaluation of the wood production potential initially consists in establishing the distribution of trees number according to the trunk circumference classes. The regression model is applied to the trees number of each circumference class. The wood production is multiplied by the density of corresponding class. The average minimal and maximal values help to estimate the average value of the wood production expressed in kgMS/ha for the three species.

[FIGURE 2 OMITTED]

Results:

Species used as firewood:

The firewood is the main domestic source of energy in Velingara-Ferlo. However, the species are not used at the same extend (table 1).

The ligneous species preferentially used for firewood in the zone are Grewia bicolor (95%), Combretum glutinosum (80%) and Pterocarpus lucens (45%). Guieria senegalensis (10%) is also used as wood of the second quality. The wood of Mitragyna inermis, Bombax costatum and Anogeissus leiocarpus are little solicited for fire. In certain villages, burning the wood of Bombax costatum and Anogeissus leiocarpa would attract the bad spirits.

Populations' structure based on circumference class:

The populations' distribution of the three species in various classes of circumference (figure 3) indicates Combretum glutinosum having the best densities except for the class [> 100 cm]. The settlement pattern of Pterocarpus lucens shows a prevalence of individuals with large diameter ([51-100 cm] and [> 100 cm]). The weak representation of individuals at small circumferences indicates a low potential of regeneration. The old individuals of Grewia bicolor belong mainly to the class [51-100 cm]. The weak representation of intermediate classes ([31-40 cm], [41-50 cm]) is related to a recruitment problem because the young individuals ([10-20 cm]) are used as fodder or firewood. This is a multi-purpose species.

[FIGURE 3 OMITTED]

Firewood production modeling:

The dry matter content averages 65.9% for Grewia bicolor, 60.8% for Pterocarpus lucens and 57.6% for Combretum glutinosum. C. glutinosum shows the higher value for water content followed by P. lucens and G. bicolor (Table 2).

The dendrometrical characteristics and the branches discs weight help in establishing allometric models for the wood production calculation per species (figures 4, 5, 6). These models were built using the regression equations i.e. P= a x [C.sup.b] (table 3).

[FIGURE 4 OMITTED]

[FIGURE 5 OMITTED]

[FIGURE 6 OMITTED]

The coefficients of determination are high ([R.sup.2] > 0.75, i.e. G bicolor: 0.93; P. lucens: 0.90 and C. glutinosum: 0.94). Indeed, these values is regarded as fort when it is higher than 0.75 (Belhedi, 2006). These coefficients measure the degree of relationship between the tree wood production and it circumference. Both traits vary concomitantly with mutual effects. The current values show the strongest correlation between the wood quantity and the circumference. In addition, a model was built by pooling the three species with the following expression (figure 7).

P = 71 x [10.sup.-4] x [C.sup.2.1471] ([R.sup.2] = 0.88) P = Wood production bois C = Circumference

This determination coefficient is lower than those from species specific models [R.sup.2] (0.88 < 0.90 < 0.93 < 0.94).

Firewood production potential:

The wood production for the three species that are mostly used as firewood species in Velingara-Ferlo were calculated using species specific established models.

P = 23 x [10.sup.-4] x [C.sup.2.8124] for Grewia bicolor

P = 66 x [10.sup.-4] x [C.sup.2.171] for Pterocarpus lucens

P = 25 x [10.sup.-4] x [C.sup.2.4658] for Combretum glutinosum

Minimum and maximum values of wood production were evaluated per class of circumference (table 3).

[FIGURE 7 OMITTED]

The G. bicolor wood production ranges from 402.3 to 1284.8 kgMS [ha.sup.-1]. The relationship between the maximum and minimal values of the wood production of this species (3) is higher than that of the two other species. Pterocarpus lucens shows the lowest minimal value (226.7 kgMS [ha.sup.-1]) and the highest maximum value. This is due to availability of higher proportion of individuals from class [> 100]. By contrast, this presents the highest standard uncertainty. P. lucens' wood production averages 1263.2 kg MS [ha.sup.-1]) while C. glutinosum shows 1338.9 kg MS [ha.sup.-1]). These species with bigger individuals are more wood producers than G. bicolor which is a shrub. Globally, both three species accounting about 91% of the firewood used in velingara Ferlo rural community produce together 3.5 tons wood per hectare. The total area of the rural community is of 261170 ha. The inhabited surface accounts for 7.6% and the classified surface, 58%. Natural formations (not inhabited and non classified) represents 65.4%, i.e. 88421 ha. Available forest trees of the three species is estimated to 309.474 tons per year (i.e. 3.5 T x 88421).

Wood consumption:

The wood consumption in Velingara-Ferlo rural community averages 1.26 kgMS per a person per day (table 5). The households' size ranges from 5 to 40 persons with an average value of 16 persons. The daily wood consumption coefficient of variation is 21.2%. Daily firewood consumption is 1.26 kgMS per person per day. The Velingara-Ferlo rural community accounts 15913 inhabitants in 2005. The annual wood consumption is 7318.4 tons per year (i.e. 1.26 kg x 15913 x 365).

Potential consumption assessment:

The study area' natural woody formations cover 95% of the energy needs. The relationship between the annual wood consumption and the available trees average 2.4% (table 6). The consumed quantities of wood account for 2.4% of the in situ available stands volumes. This parameter helps in testing the natural formations capacities to satisfy the rural population firewood needs and requirements. The increased rate of the natural population (2.8%) and the annual decrease of sahelian natural formations (0.67%) [8] were integrated for modelling over 25 years (table 6). In 2030 the annual wood consumption will double while the production potential will have dropped by 15.4%.

Discussion And Conclusion:

The goal of this work was to identify the three species mostly used for firewood in Ferlo, to estimate firewood consumption and to evaluate the potential wood production using allometric models for production. Grewia bicolor (95%), Combretum glutinosum (80%) and Pterocarpus lucens (45%) are preferred for firewood in the zone because of their wood physical characteristics (hardness, density, and calorific value), the convenience (little smoke and more flame), availability of the three species. Also its offer qualified charcoal. The various dry matter rates in wood of these species are related on physical characteristics (hardness and density) different but also to nature from the edaphic substrate and the water availability in the ground. According to Renaud (2006), the ecological factors determining the creation of woody matter are numerous such as the tree age, soil conditions (ground, climate), the water availability or wood density together with individual genetic factors. The comparison of the various models developed reveals a certain difference. Indeed we compared the models of the three species studied between them and with the model from pooled species to know whether a single model is employable for the three sahelian firewood species as previously did by Auclair and Metayer [2] on three firewood species such as Carpinus betulis L, Betula pubescens Ehrh. and Quercus robur L.). The comparison of the three models showed an impossibility of using a tariff for the three firewood species. However, it should be noted that the tariffs of Grewia bicolor and Combretum glutinosum are a little similar, but different from the model for the pooled firewood species. Indeed, the tariffs obtained depend on the firewood species [16,2], the tree morphology and the morpho-pedological conditions. The results obtained are interesting for practices in a context of increase in rural request for forest products (firewood, wood of service). Today, the challenge of the sylvo-pastoral ecosystems sustainable management in Ferlo is to reconcile the production with the populations needs. Therefore, knowing the potential of production of these ecosystems are required as well as the wood quantities consumed. Moreover, the three species studied are overexploited because of their attractive utility. Indeed Grewia bicolor and Pterocarpus lucens that are preferred for firewood are also higly grazed by cattles, but also most pruned by the shepherds; they are multi-purpose species. Each day of the trucks charged with this wood of good quality leaves the zone to supply the great urban centres.

Globally, the firewood is still available and women are charged on the collection. There is no regulation and the women seem to be worried more the collected wood transportation than that of its availability. Average firewood consumption is of 1.26 kg per person per day in the rural community of Velingara-Ferlo. These results are comparable with those found in Chad (1.14 kg per person per day) [20], but they are higher than those from Niger native rural environment, i.e. 0.8 kg per person per day [10] and 0.6 kg per person per day [1]. In spite of the gap between our results and those from Niger, it seems that they fit all in the usual standards of general average of wood consumption in Africa in the southern Sahara as defined by Taga [22] i.e. 0.6 to 1.5 kg per person per day. The use of the allometric models made help to evaluate the production and productivity of the three characteristic species which account for 91% of the firewood consumed in the rural community of Velingara-Ferlo. The aggregate output of the three firewood species is of 3.5 tons [ha.sup.-1]. These results corroborate those from Ada and Mahamane [1] in the formations of Combretaceae in Niger (3.3 tons [ha.sup.-1]) and by the Project ED I.S. Ltd [18] in the dry Sudanese wooded area of Chad (3.5 tons [ha.sup.-1]). The trend in the potential of wood production of the ecosystems is an indicator of the human pressures on natural resources. The quantities of wood actually exploited in one year (7318 tons) account for average 2.4% of the capital tree (309474 tons). In Chad, estimation varies according to authors, although the magnitude around 5% of the capital tree [22]. Indeed, exploitable wood volumes must represent more 5% of volumes in forest stand not to put in danger the inheritance of the woody resources. By comparing our results with those obtained in these ecosystems. It can be said that the woody resources are still overall sufficient to satisfy the population needs. This situation is explained by the extent of the rural community (5 times the area of Dakar) and by a very low density (6 inhabitants [km.sup.-2]) compared to the national average i.e. 48 inhabitants [km.sup.-2]. However, in 25 years, the ratio of wood consumption to total tree quantity would be over than 5.6%, i.e. the demand will be higher than the offer and that the woody resources inheritance would be threatened. The ratio of wood consumption to the total tree quantity appeared as indicator of the uptake rate of the wood resource. It is a good indicator to study the ecosystems sustainability but also the balance between the needs of wood for the rural populations and production capacity for the sylvopastoral ecosystems [14]. However, the transfer of the models suggested to other areas must be made prudently. Many parameters are to be considered in building the models of production like the tree state and the soil type [11]. Also, a great exactitude is not attainable generally with allometric models.

References

[1.] Ada, L., & A. Mahamane, 1999. Les ressources forestieres naturelles et les plantations forestieres au Niger. EC/FAO ACP Collecte de donnees--Rapport Technique AFDCA/TR/13: 46.

[2.] Auclair, D. & S. Metayer, 1980. Methodologie de l'evaluation de la biomasse aerienne sur pied et de la production en biomasse des taillis. Revue Acta OEcologica, 1(4): 357-377.

[3.] Belhedi, A., 2006. La correlation et la regression simples courbes. FSHS. Universite de Tunis. Site internet http: www.kokoom.com

[4.] Clement, J., 1982. Estimation des volumes et de la productivite des formations mixtes forestieres et gramineennes tropicale. Bois et Forets des Tropiques, 198(4): 35-58.

[5.] Cornet, A., 1992. Relation entre la structure spatiale des peuplements vegetaux et le bilan hydrique des sols de quelques phytocenoses en zone aride. In L'aridite une contrainte au developpement. ORSTOM, Editions, pp: 245-263.

[6.] Coulibaly, S.M., 1998. Determination de la productivite des jacheres dans la zone de Ouellessebougou. Memoire de fin de cycle. Institut Polytechnique Rural de Formation et de Recherche Appliquee (IPR/IFRA) Katibougou, Mali, 67 p.

[7.] FAO, Projet GCP/INT/679/EC.

[8.] Fries, J. & J. Heermans, 1990. Amenagement des forets naturelles en Afrique semi-aride : situation actuelle et besoins de recherche. Atelier FAO sur l'amenagement et la gestion participative des forets naturelles en zone sahelienne. Ouagadougou (Burkina Faso).

[9.] Jayaraman, K., 1999. Manuel de statistique pour la Recherche forestiere. FAO--Cooperation hollandaise--Commission europeenne: p: 239.

[10.] Lawali Mahamane, E.M., 1994.--Le bois energie au Niger : connaissances actuelles et tendances. FAO, Projet GCP/TNT/679/EC.

[11.] Manlay, R., R. Peltier, M. Ntoupka & D. Gautier, 2002. Bilan des ressources arborees d'un village de savane soudanienne au Nord Cameroun en vue d'une gestion durable. In Savanes africaines : des espaces en mutation, des acteurs face a de nouveaux defis. Jamin J. Y.Seiny Boukar L. (editeurs scientifiques): Actes du colloque, mai 2002. Maroua, Cameroun: pp: 15.

[12.] Nasi, R., 1994. La vegetation du Centre Regional d'endemisme soudanien au Mali. Etude de la foret des monts mandingues et essai de synthese. These Doct. Sci., Paris Sud: 175 p + annexes.

[13.] Newbould, J.P., 1967. Methods for estimating the primary production of forest. Blackwell. Oxford, pp: 62.

[14.] Ngom, D., 2008. Definition d'indicateurs de gestion durable des ressources sylvopastorales au Ferlo (Nord-Senegal). Doctorat de 3eme Cycle en Biologie Vegetale. option: Ecologie/UCAD, pp: 148.

[15.] Nouvellet, Y., 1992. Evolution d'un taillis de formation naturelle en zone soudanienne du Burkina Faso. Bois et Forets des Tropiques, 237: 45-59.

[16.] Phillips, D.R., 1977.Total tree weights and volumes for understory hardwoods. TAPPI. 60: 68-71.

[17.] Picard, N., M. Ballo, F. Dembele, D. Gautier, M. Kaire, M. Karembe, A. Mahamane, R. Manlay, D. Ngom, M. Ntoupka, S. Ouattara, P. Savadogo, L. Sawadogo & J. Seghieri, 2006. Evaluation de la productivite et de la biomasse des savanes seches africaines: l'apport du collectif SAVAFOR. Bois et Forets des Tropiques, 60(288): 75-80.

[18.] PROJET ENERGIE DOMESTIQUE. 1996. Inventaire du bois de chauffe dans la region de Ndjamena. Compte rendu final. I.S.Ltd. p: 32.

[19.] Renaud, A., 2000. Cartographie du volume ligneux des peuplements de la foret boreale a l'aide de donnees d'altimetrie Laser. Memoire de maitrise Geographie, Universite du Quebec a Montreal., p: 113.

[20.] REPUBLIQUE DU TCHAD. 1994. Comite Directeur de suivi de la strategie pour l'energie domestique, plan d'action detaille, mai p: 40.

[21.] Sylla, m.L., 1997. Evaluation rapide de la productivite et de la production des formations vegetales: bassins de Bamako et de Segou. Rapport de mission. Republique du Mali/MDRE/DNAER: p: 27.

[22.] Taga, H., 2000. Rapport d'etude sur les donnees du bois-energie au Tchad. EC/FAO ACP Collecte de donnees--Rapport Technique AFDCA/WE/05. Serie Forestry Statistics and Data Collection., p:32.

(1) Daouda NGOM, (2) Amy BAKHOUM, (3) Valentin KINDOMIHOU, (2) Sekouna DIATTA, (2) Leonard Elie AKPO

(1) Department of Agroforestry, University of Ziguinchor, Po. Box: 523 Ziguinchor, Senegal,

(2) Laboratoire d'Ecologie et Hydro-ecologie, Faculte des Sciences et Techniques, Universite Cheikh Anta DIOP, Senegal, B.P. 5005 Dakar (Senegal)

(3) Laboratory of Applied Ecology, Faculty of Agronomic Sciences, University of Abomey-Calavi, 03 BP1974 Cotonou, Benin

Corresponding Author

Daouda NGOM, Department of Agroforestry, University of Ziguinchor, Po. Box: 523 Ziguinchor, Senegal,

E-mail: ngom_daouda@yahoo.fr
Table 1: Importance of the preferred
species for firewood (FR %)

Species                 Frequence (%)

Grewia bicolor          95
Combretum glutinosum    80
Pterocarpus lucens      45
Guieria senegalensis    10
Anogeissus leiocarpa    5
Dalbergia melanoxylon   2.5
Balanites aegyptiaca    2.5
Mitragyna inermis       0
Bombax costatum         0
Pterocarpus erinaceus   0
Sclerocarya birrea      0
Lannea acida            0

Table 2: Wood dry matter and water contents of the different species

Species                Dry matter content (%)   Water content (%)

Grewia bicolor         65.9                     34.1
Combretum glutinosum   57.6                     42.4
Pterocarpus lucens     60.8                     39.2

Table 3: Woody production models for Grewia bicolor,
Combretum glutinosum and Pterocarpus erinaceus

Variables              A        b       [R.sup.2]

Grewia bicolor         0.0023   2.812   0.87

Pterocarpus lucens     0.0066   2.171   0.81

Combretum glutinosum   0.0025   2.466   0.88

Variables              Modeles

Grewia bicolor         P = 23.[10.sup.-4]
                       x [C.sup. 2.8124]

Pterocarpus lucens     P = 66.[10.sup.-4]
                       x [C.sup. 2.171]

Combretum glutinosum   P = 25.[10.sup.-4]
                       x [C.sup. 2.4658]

Table 3: Variation of the production according to trees trunk
circumference for species

Class of        [10-20]        [21-30]        [31-40]
circumference
(cm)

                Min    Max     Min    Max     Min     Max

P (kg MS/ha)    5.8    40.8    21.8   59.4    69.8    143
G. bicolor

P (kg MS/ha)    18.9   104.1   89.8   216.3   148.7   278.7
C. glutinosum

P (kg MS/ha)    0.7    3       2.7    5.9     14.3    24.8
P. lucens

Class of        [41-50]         [51-100]         [>100]
circumference
(cm)

                Min     Max     Min     Max      Min      Max

P (kg MS/ha)    241.7   422.3   688.7   4575.8   1385.8   2467.6
G. bicolor

P (kg MS/ha)    250.2   408.2   874     4598.2   943.3    8136.3
C. glutinosum

P (kg MS/ha)    35      53.8    196     845.7    1111.7   12865.1
P. lucens

The average values of minima and maxima per class of circumference
is used in calculating the average wood production expressed in
kgMS [hectare.sup.-1] ([+ or -] Standard Errors) (table 4) for both
species.

Table 4: Estimation of average wood production of the three forest
species (kgMS [ha.sup.-1])

Species       Minima           Maxima            Means

Grewia        402.3 [+ or -]   1284.8 [+ or -]   843.5 [+ or -]
bicolor       27.2             51.9              47.7

Combretum     387.5 [+ or -]   2290.3 [+ or -]   1338.9 [+ or -]
glutinosum    20.9             70                67.9

Pterocarpus   226.7 [+ or -]   2299.7 [+ or -]   1263.2 [+ or -]
lucens        29.2             108               103.3

Table 5: Firewood consumption in kg [person.sup.-1] [day.sup.-1]

Households       Consumption       Number of   Consumption
                 kg [day.sup.-1]   persons     in kg per
                                               person per
                                               day

1                20                20          1.00
2                25                20          1.25
3                16                9           1.78
4                16.7              17          0.98
5                16                18          0.89
6                14                10          1.40
7                12                8           1.50
8                14                8           1.75
9                8                 7           1.14
10               16.7              14          1.19
11               30                25          1.20
12               12                8           1.50
13               12                10          1.20
14               33.3              40          0.83
15               33.3              32          1.04
16               20                18          1.11
17               20                14          1.43
18               6                 5           1.20
19               15                9           1.67
20               33.3              30          1.11
average value    18.67             16.1        1.26 kg per
                                               person per day
Coefficient of                                 21.20 %
variation

Table 6: Firewood offer and demand characteristics in the
CR of Velingara-Ferlo

Measured traits       2010                    2035

Population            15913 inhabitants       31738 inhabitants
Forest Wood Capital   309 474 tons of dried   261892 tons of dried
                        wood [an.sup.-1]        wood [an.sup.-1]
Woody dairy           1.26 kg per person      1.26 kg per person
  consumption           per ha                  per ha
Annual woody          7318.4 tons of dried    14596 tons of dried
  consumption           wood [an.sup.-1]        wood [an.sup.-1]
Consumption balance   2.4 %                   5.6%
  per production
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Title Annotation:ORIGINAL ARTICLE
Author:Ngom, Daouda; Bakhoum, Amy; Kindomihou, Valentin; Diatta, Sekouna; Akpo, Leonard Elie
Publication:Advances in Environmental Biology
Article Type:Report
Geographic Code:6SENE
Date:Jul 1, 2012
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