E.H. Sène
El Hadji Sène is Chief of the Forest and Wildlands Conservation Branch of the Forest Resources Division. FAO Forestry Department.
There is a growing awareness in Africa of the need for peri-urban woodlands and parks to satisfy physical and material needs and for leisure and recreation. This need is changing in accordance with African urbanization which, from a modest 18 to 21 percent between 1950 and 1970, jumped to 32 percent in 1984. The limitations on forest management and sustainability still prevent maximum leisure and recreational use but the situation is rapidly improving, as is forestry's capacity to provide urban populations with products, employment and income.
Africa is a "young" continent; the traditional links between populations and their environment, particularly the trees and forests, are very much alive; considering both their food and commodity as well as their spiritual and cultural aspects. These links influence and will continue to influence strongly the provisions and measures introduced by modern administrations to define the status and role of trees and forests in and around urban areas.
The evolution of traditional links
The link between trees and forests and inhabited areas varies according to ecological conditions. In countries characterized by closed forests, the traditional housing pattern was one of dispersed units; the establishment of a village was generally at the expense of trees and woodland. Most villages or small towns in forest areas are conspicuously short of or devoid of trees which are not really felt to be needed, as they are oppressively present in the surrounding environment.
The situation, however, is different in open forests, savannahs and steppes. Trees have played an important symbolic role in the establishment of ancestral villages in the Sahelian and Sudanese zones. A tree or cluster of trees was considered propitious for settlement, whether as evidence of water availability, land fertility, abundance of game or simply as a parasol that allowed restful shelter. The names of many towns and large villages in the Sahel stem from trees.
Once the villages have been established, the neighbouring forest serves for agricultural, hunting, fuelwood and medicinal purposes. The spiritual needs of meditation and hidden recesses for initiation rites are the best guarantees of forest conservation near human settlements, which explains the common existence of forest remnants near towns. It also explains the continued existence of trees that no longer fit in a completely urbanized space and environment. A certain tamarind tree (Tamarindus indica) was long venerated in the centre of Kaolack in Senegal, for example. When it died, its stump was left for many years to wear away slowly and naturally.
Trees also have an economic role. They are never cut down in the Sahel, where there is a direct dependence on their products for food. The baobab, the shea tree, the borassus (Borassus aethiopum) and the doum palm (Hyphaene thebaica) signal the presence of African villages from afar. The location of old and now-vanished villages is also indicated by clusters of baobab trees, for this calciphile species only occurs naturally in stands over limestone soil; elsewhere, baobab, clusters indicate earlier human settlements. The tree also has an important social role, belying the misnomer "palaver tree", which unfairly implies endless talk and even idleness. In fact, this tree plays a central and noble role in African life, serving as the community meeting place for consultation, discussion, education and also for the lighter side of rest and recreation.
Modern needs induced by urban expansion
Most towns in the Sahel have grown in a relatively unplanned way, with considerable improvisation in response to the influx of rural migrants seeking the mirage of a better life in the city. Town planners and urban populations have gradually come to be increasingly concerned by the following six aspects of trees and forests in an urban context.
Trees, towns and the use of urban ant peri-urban land. The rapid development of towns in developing countries often takes place in areas where land tenure has not been fully settled and where long term or, indeed, medium-term planning is not part of the equation. Conflicts concerning land use are therefore frequent. Problems of peri-urban land-use planning and regulation are particularly important in the Sahel countries.
Urban planners are now, however, trying to make up for lost time. Since the early 1900s, Dakar, a pioneer among Sahel cities, has had a series of master plans to govern the interface between urban and undeveloped land in an attempt to cope with heavy population pressure. Their implementation has been only partial at best, given the swift rise of shanty towns, unauthorized building and the race for the fait accompli, all of which have left little scope for the planning of green areas.
Neem trees line a peri-urban thoroughfare leading towards Dakar, Senegal
The other large towns in the Sahel enjoy relatively open spaces, despite the proximity of natural constraints or difficult settings (the banks of the Niger for Bamako and Niamey and the banks of the Chari for N'Djamena).
Urban sanitation development and plantations. Towns that spring up and grow rapidly usually face severe environmental sanitation problems as population increases far outstrip the development of needed infrastructures. Sahelian towns all have problems of swampy or temporarily flooded land, unstable slopes along coastlines or riverbanks and encroaching sands. All these problems have been encountered in Dakar (see Box): the main objective of the Hann Forest Park was to drain the Hann marshlands and lowlands and protect the aquifer; wells were sunk to provide drinking water to the town of Gorée. The Greater Dakar Urban Development Service (STAGD), the partial forerunner of the Parks and Gardens Service in Senegal, was responsible for stabilizing the coastline by planting trees.
Urban and peri-urban woodlands in Dakar: underutilized and endangered The city of Dakar was founded in 1857. Word has it that the small fishing village at the time owed its name to a little evergreen that is well known in the Sahel, the tamarind (Tamarindus indica). What is more certain is that the picturesque market in the heart of the capital, the "Sandaga", owes its name to another evergreen, the "sand" (Morus mesozygia) and that Portuguese sailors following the coastline noticed that the peninsula was particularly green and called it Cabo Verde. The different concerns of the various administrators of the island of Gorée? Dakar and its peninsula led to early land management, with the result that, today, the city has an excellent although not fully tapped - potential to develop an enviable system of parks, green areas and peri-urban woodlands. · Even at the beginning of the century, the Hann marshland, 7 km from the centre, was essentially developed as a water reservoir for Dakar and Gorée. Permanent wells were subsequently sunk and the 80 ha Hann woodland park was developed to serve as the headquarters of the General Forests Inspectorate of French West Africa. Yet, it also served as a recreational park and featured a small botanical garden and zoo for the benefit of Dakar's residents. In 1943, the colonial governor recognized the need to use brushwood and multispecies plantations to stabilize and embellish the coast to the east and west of the capital. The Dakar coastal headlands (Corniches) area was officially established in 1943 and abundantly planted, particularly in the east. Its western part, facing the Madeleine Islands National Park, is now under careful land-use management. · The Mbao reserve forest was established in 1940 over an area of 770 ha, although it was reduced to some 500 ha in 1970 to make way for Dakar's industrial zone. This prime peri-urban woodland is threatened by strong population pressure and particularly inadequate land-use planning. · The coastal areas. Reforestation was officially introduced over an area of more than 4000 ha along the sandy beach area of the capital in 1950. Its purpose was to fix the sand dunes and protect the coastal system (Malika, Retba, Cambérène). More than 2000 ha have been lost to construction (the Cambérène and Yoff areas) but the attractive filao plantations, which cover more than 1000 ha at a distance of less than 30 km from the city, are prime peri-urban woodlands. · A final belt with peri-urban woodland potential includes the forest of Deny-Youssouph (400 ha), the forest of Sebikhotane (520 ha) and the Dialao hills, which are under threat from quarrying activities. The urban triangle of Dakar-Mbour-Thiès. This triangle of towns less than 80 km from each other will become a megalopolis in 50 years, time. Land-use planning should be introduced now so that a large part of the existing reserved forests, covering more than 10000 ha (Pout, Thiès, Bandia, Nianing and Pointe Sarène), are maintained, reforested and equipped with facilities, and so that the natural stands (particularly of Acacia seyal) are rehabilitated. Tourist development along the Petite Côte and the immense needs foreseen for the future call for rigorous action now, especially along the lines of the extensive plantations, embellishment and road operations undertaken by the Société d'Aménagement de la Petite Côte (SAPCO). The potential for Dakar and the urban triangle is excellent if measures are taken soon - in ten years, time it will be too late. |
Sahelian towns have to resist sand and dust encroachment every day. Vegetation buffers the impact of wind and sand, while the planting of stands, clusters and shelter-belts has become a common practice. The so-called green belt plantations in Nouakchott and the sand dune fixation plantations in the southern third of Senegal's Grande Côte are all essentially sand and dust protection devices. In the Niger, the peri-urban plantations of Niamey, of small towns such as Tahoua or of large villages such as Dogondoutchi serve to protect and develop the urban environment while also offering sources of fuelwood and timber.
Fuelwood supplies, pen-urban forests and plantations. While land clearing for rain-fed cultivation is what causes the greatest disturbance to plant formations in the rural Sahel, the need for fuelwood is the decisive factor that influences and governs the continued existence of natural forests, plantations and single trees in the peri-urban environment. The towns have gradually pushed back the forest to meet the greater need for fuelwood and charcoal which has accompanied galloping population growth. In Senegal, urban charcoal consumption alone is officially estimated to be 900000 m3 of wood but is probably more than 1500000 m3, which would correspond to 3000 to 5000 ha of savannah and steppe over a radius of 60 to 600 km from the town! Fuelwood production is therefore an obvious function that cannot be ignored in the design of urban and peri-urban forest systems in this subregion.
Systems to conserve natural forests for fuelwood supply or to plant trees to meet urban fuelwood needs have been the most common components of cooperation agencies and African government forestry and energy strategies during the last 20 years, particularly in arid and semi-arid areas (Leach and Mearns, 1988). Since 1950, forest development in Senegal's Bandia forest in the Dakar-Mbour-Thiès triangle, located less than 50 km from each of these towns, has centred on the production of fuelwood. In all other Senegalese forests that are too remote to be considered peri-urban and where some form of management has taken place, the focus has been on supplying fuelwood to urban areas, particularly Dakar. In Burkina Faso, the inventory and management of natural forests near Ouagadougou for fuelwood, started in 1981, offers a good example of forestry oriented towards both urban energy needs and the promotion of rural community participation.
The plantations or peri-urban green belts established around many towns in the Sahel before and particularly after 1970 focus primarily on fuelwood and other "environmental" objectives: eucalyptus plantations around Ouagadougou; plantations around Bamako (the Monts Mandingues forests for the mixed production of building poles, timber and fuelwood); peri-urban plantations in Niamey, based on eucalyptus as well as other species; and around N'Djamena, neem, rosewood (Dalbergia sisoo) and cailcedra (Khaya senegalensis) plantations as well as the reintroduction of protected Acacia seyal stands.
The socio-economic aspects of peri-urban fuelwood plantations are, however, complex and warrant close attention. The peri-urban land area is coveted for other purposes that produce quicker returns than fuelwood: fruit orchards and market gardens, building lots, land speculation and property development. Unless deliberate decisions are taken to defend forestry and unless realistic prices are set for wood (at least partially), it will be difficult to maintain or allocate peri-urban land to forest-oriented use.
Peri-urban forests for a sustained flow of locally produced and traditionally consumed products. The transfer of rural populations to urban areas does not necessarily mean a rapid change in consumption patterns. The consumption of popular forest foods in the large towns (baobab leaf, tamarind, processed Parkia seeds, etc.) is virtually identical to the products on sale at a rural market. Palm trees are tapped for palm wine (Dakar, Thiès). In the forest of Mbao, 15 km from Dakar in Senegal, local species whose leaves, bark or roots have medicinal use are intensively exploited and could become endangered species (Anthostema senegalensis, the Tinospora bakis creeper and the rutaceous Fagara xanthoxyloides, to name but a few). The uses of natural formations in peri-urban forest systems should influence management and development decisions. Thus, participatory management of the Guesselbodi forest, close to Niamey in the Niger, included both the collection of stubble for urban rearing of small livestock, and the picking of wild fruit. The management of the Monts Mandingues forest could benefit considerably from a greater emphasis on everyday consumer products such as the fruit of the Saba senegalensis (a very hardy species abundant in cultivated and fallow areas) for which there is a high and certainly unsatisfied demand in Dakar and Bamako.
These observations confirm that the peri-urban forests in the Sahel should be used for multiple purposes.
Species used in Sahelian urban forestry
Species |
Use |
Origin |
Degree of use |
Acacia holosericea |
Fences, street trees |
i |
* |
Acacia sp. |
Ornamental |
L |
** |
Araucaria sp. |
Ornamental |
i |
** |
Azadirachta indica |
Shade, street trees |
i |
**** |
Bauhinia thonningii |
Ornamental |
i |
* |
Bauhinia sp. |
Hedges, ornamental |
L |
|
Bombax costatum |
Ornamental |
L |
*O |
Cassia siamea |
Street trees, shade |
i |
** |
Casuarina equisetifolia |
Shade, street trees |
i |
**® |
Ceiba pentandra |
Ornamental |
s |
**¯ |
Cordia sp. |
Ornamental |
i |
** |
Combretum paniculatum |
Ornamental |
L |
*O |
Crescentia cujete |
Ornamental |
i |
*O |
Cycas sp. |
Ornamental |
i |
* |
Dalbergia sissoo |
Ornamental |
i |
*O |
Delonix regia |
Ornamental |
i |
**¯ O |
Eucalyptus spp. |
Ornamental, other |
i |
*** |
Ficus thonningii |
Shade, ornamental |
L |
**¯ O |
Gaiacum officinale |
Ornamental, fences |
i |
** O |
Gmelina arborea |
Ornamental, shade |
i |
** |
Grevillea robusta |
Ornamental |
i |
* |
Hura crepitans |
Ornamental, street trees |
i |
**O |
Khaya senegalensis |
Shade, ornamental street trees |
L |
***¯ O |
Leucaena sp. |
Ornamental, fences |
i |
** |
Lonchocarpus sericeus |
Ornamental, fences |
i |
** |
Melia azedarach |
Ornamental |
i |
*O |
Moringa pterigosperma |
Ornamental, food |
i |
**O |
Peltophorum sp. |
Shade |
i |
*¯ |
Pithecellobium dulce |
Hedges, shade |
i |
*O |
Prosopis (chilensis + juliflora) |
Hedges, shade (in the north) |
i |
*** |
Sapindus saponaria |
Ornamental, religious |
i |
**¯ O |
Spondias purpurea |
Ornamental, fences, fruit, shade |
i |
*¯ O |
Tamarix sp. |
Shade, ornamental |
L + i |
* O |
Tecoma pentaphylla |
Shade, ornamental, street trees |
i |
**¯ O |
Tecoma stans |
Ornamental, gardens |
i |
* |
Terminalia catappa |
Ornamental, shade |
i |
** |
Terminalia mantaly |
Ornamental |
i |
*** |
Thespesia populnea |
Ornamental |
i |
*¯ |
i = introduced (exotic);
L = local (indigenous);
s = subspontaneous;
* = little used;
** = used moderately;
*** = heavily used;
**** = used predominantly
® ¯ = stable, increasing or decreasing trend;
0 = underutilized potentialNote: The table shows the extreme weakness of local or indigenous species used in plantations or for ornamental purposes in three Sahelian cities. There are, however, numerous species with important potential for aesthetic improvement of cities: Combretum spp., the many species that Dour in the cool and dry season, for example the genera Stereospermum knuthianum, Lonchocarpus, Bombax; the indigenous Anacardiaceae, in particular the Lannea numerous acacias, and many other species than can be rooted from cuttings. A programme of horticultural research could contribute to the fuller exploitation of this tragically underutilized potential.
Urban and peri-urban forests for pleasure, recreation and relaxation. The fact that this aspect is at the tail end of the list is not fortuitous, for the ornamental, leisure, exercise and relaxation dimensions in forestry have only recently emerged in the Sahel and elsewhere in Africa. The role of trees and forests in recreation and urban embellishment has only come to the fore during the past 20 years. Rapid urban growth has been accompanied by housing development programmes in some countries; in modern areas built without any planned green areas, people soon felt the need to plant large numbers of trees. Unfortunately, these plantation efforts have taken place without sufficient preparation on the part of the urban park and forest services.
As mentioned, change has come very quickly and a number of new species (see Table) now feature alongside the neem, the cassia and the coral tree which were the pioneer urban species. The design of urban plantations has also changed, with large monospecific stands now being landscaped and integrated with other leisure facilities.
The recreational functions of actual urban and peri-urban woodlands are still quite tentative, although there are of course examples of well-established forests that have had a recreational role since colonial times. For example, in Burkina Faso the famous 500 ha Bois (referred to as the "Bois de Boulogne"), which once lay at the gates of Ouagadougou but is now virtually in the city centre, is a magnificent green haven for leisure activities and walks. In certain parts, the Prosopis plantations in the Nouakchott green belt (in Mauritania) are attractive woodlands suitable for relaxation and picnicking.
On the whole, each major town in the Sahel has forest and wooded areas that are already being used by the urban populations for walks and relaxation. However, the government authorities, municipalities and neighbourhood associations have not yet fully come to grips with this aspect of forestry and appropriate management and equipment initiatives do not yet cater for the existing or potential demand.
Urban green areas for income and employment. Tree-planting, urban park maintenance and the use of peri-urban forest products generate a substantial number of jobs in the Sahel. The urban unemployed are organizing and finding decent employment in tree maintenance work using rudimentary equipment for pruning, treatment and caterpillar removal. Some remove fallen trees while others recover the wood from fallen trees for recycling as fuelwood or handicraft and construction wood. A number of park and garden undertakings provide seasonal employment to many unemployed people. Besides fuelwood, the gathering of fruit, mushrooms and plants for traditional medicines and the sale of green forage or straw are important sources of income that, unfortunately, have not yet been quantified.
The development and promotion of urban trees and peri-urban forests and woodlands, and particularly the optimum use of existing resources, are hampered by a number of constraints.
The need to improve the protection of urban trees. Urban trees are often degraded, calling for the introduction or reinforcement of education programmes. Uncontrolled grazing is still a serious problem. Draconian animal impounding laws and fines for the owners of stray animals, measures introduced by a prefect in Tahoua in the Niger, have set a rigorous example for enforcing civic respect for the environment.
However, the management of urban trees and parks also concerns the various utility services (sanitation, water, power and telephones) which should combine their interventions and reduce inopportune ditch-digging and unsightly and unauthorized urban tree-cutting to a minimum.
Water supply and enhanced planting practices. Urban tree-planting should be accessible to everyone. An essential objective of urban green areas and extension services should be to promote species that require little water but are of ornamental value.
Trees are prominent in this view of Nioro du Sahel, located in western Mali
The use of interurban and peri-urban stands. The absence of multipurpose urban and peri-urban forest management is the main obstacle to the promotion of urban forestry. The lack of municipal resources and the fact that forestry services have concentrated on production have totally eclipsed recreational peri-urban forestry. Rapid change is both necessary and feasible, as current progress in dry forest management in the Sahel merely needs to be supplemented by a landscape and recreational dimension to be able to open the way for authentic urban forestry.
Genuine grassroots participation. Participation in tree-planting has featured prominently in people's advancement programmes since independence, with all the symbolism and easy patriotic appeal of the tree. "Tree Days" and "Forest Weeks" have emphasized the role of the forest and of ornamental or shade trees in homes, public squares, streets and along roads. The objectives of these grassroots tree-planting campaigns have gradually broadened and diversified to include the more economic aspects. In Senegal, for example, the change from "Forest weeks" to "People's Reforestation Actions" in the early 1970s reflects a change to accommodate the integration of agriculture and the production of fuelwood and non-wood products - a prelude to today's participatory forestry. Unfortunately, however, this development has not been mirrored in urban forestry. Although rural forestry projects have spilled over into urban forestry, direct popular and municipal participation does not extend far beyond urban beautification and greening operations. The so-called "Set-Setal" movement of young Senegalese town dwellers, based on a philosophy of personal and environmental cleanliness, has mobilized young people to clean up and embellish town neighbourhoods and has greatly improved the situation, at least in Dakar. Initiatives to increase awareness of the usefulness of and need for forests and woodlands in urban and peri-urban areas (green havens) are needed everywhere. This is not easy, as housing needs are so great and pressing that calls for the shared use of urban land might well seem absurd.
Peri-urban forestry: the institutional gap. Forestry administrations have failed to consider the landscape and recreational dimension of peri-urban forests, not so much because landscape architects have not been trained but rather because there has been a complete or partial unawareness of institutional responsibility in this area. Landscape units should be established within the forestry services, or else the urban park services should include peri-urban forests. The first option would seem to be the most feasible and rational in the present circumstances. Having understood the need for both diversified forestry objectives and participation, the forestry services should extend their good performance in the Sahel to include the amenities of recreation and relaxation.
Peri-urban forestry in the Sahel has not yet gone beyond the needs of energy supply to give decisive and active consideration to questions of leisure and recreation. Yet, currently available resources would permit a number of peri-urban forest use options, for each Sahelian capital has natural or cultivated woodlands that could be developed and equipped for the growing recreational needs of urban populations. This is the time to introduce stringent measures; first, to protect the forests from speculation, then to ensure that basic urban forest and park recreational facilities are provided and personal safety needs met. On the institutional level, forestry administrations will now have to consider "urban forestry" as a specific component in its own right, leaving decorative city planting to the parks services. Appropriate training will of course be required, as will research to broaden the range of species and to improve and disseminate methods of planting under the all-too-familiar conditions of drought.
CILSS/UNSO/FAO. 1976. Consultation sur le rôle de la forêt dans un programme de réhabilitation du Sahel - Dakar, Senegal, 26 April-1 May 1976. Ouagadougou, CILSS.
Government of Kenya. 1992. Forestry Master Plan. Annex VI: Bioenergy. Nairobi, Government Printing Office.
Guèye, I. & Laban, P. 1992. Des bois de villages a la gestion du terroir villageois en Afrique de l'Ouest. London, IIEO.
Guinko Sita, P. 1992. Récolte et commercialisation des produits non ligneux des essences forestières locales dans le département de Zitenga, province d'Oubritenga (Burkina Faso). Proc. Tenth World Forestry Congress. Nancy, France, Ministry of Agriculture and Forests.
Hoeringer, P. 1980. L'arbre dans la ville. Lecture sociale en quatre tableaux du couvert végétal dans la ville africaine. L'arbre en Afrique tropicale: la fonction et le signet. Cahiers de l'ORSTOM, Série Sciences humaines, Vol. XVII, n° 34. Paris, ORSTOM.
Leach, G. & Mearns, R. 1988. Beyond the fuelwood crisis: people, land and trees in Africa. London, Earthscan Publications.
N'Diaye, A.L. 1983. Problématiques du bois de chauffe dans les pays sahéliens, Vol., I. Dakar, CPU-Sahel.
Savané, L. 1988. Populations: un point de vue africain. Anvers, Editions EPO.
Sène, E.H. & Baba, D. 1970. Communication relations ville-campagne. Colloque CENECA "Le monde rural, gardien de la nature". Paris, CENECA.
Sène, E.H. 1985. Trees, food production and the struggle against desertification. Unasylva, 37(150): 19-26.
Sène, E.H. 1991. Sahel, Quando l'albero è vita. Cooperazione, 103. Rome, Ministry of Foreign Affairs.