Livestock production challenges in the rangelands ecosystem of South Sudan Prof. A.L. Abate abateal@yahoo.com Paper presented at the Workshop on Environmental Management Plan for Post-conflict Sudan, Raha Hotel, Juba, South Sudan, October 31-November 2nd, 2006 Abstract The rangelands of South Sudan boast a large number of animals available in significant numbers in all livelihoods zones except the tsetse fly infested southwesterly Green Belt where only small ruminants may be found. The communities who keep the livestock also grow crops in a closely linked agro-pastoral production system. A sophisticated rhythm of seasonal mobility, perfected over generations, has sustained a large number of animals in the range, which by recent counts includes about 8 million cattle. Thus, not only do the rangelands contribute to the livelihoods of the local inhabitants, they are also the basis of a livestock industry with huge potential for export trading. A number of measures are discussed for sustainable utilization of the range while protecting the environment. Among these are the need to understand, through research, the variability and diversity of the agropastoralist system and efficient management of water resources, grazing and animal populations. A number of areas requiring enabling policies are pointed out. Introduction With an area of 640,00.00 km2 and a population estimated at 5.3 million in 1998 (FAO, 1998) and most probably around the 8.0 million mark, at present, South Sudan is endowed with immense mineral and agricultural wealth. Deliberate and consistent neglect, mismanagement, marginalisation and underdevelopment, over 50 years, by successive regimes meant that the natural resources sector of the area, excepting recent exploitation of its oil reserves, has not been open to investment and development. Following the signing of the Comprehensive Peace Agreement in 2005, there have been concerted efforts on the part of the Government of Southern Sudan (GOSS) to revitalize various sectors of the Southern economy and particularly its agriculture on which the majority of the people depend for their livelihoods. Livestock production, a major component of agriculture, has been subjected to numerous shocks including intra- and inter-communal raiding, looting, shortages of grazing due to drought and seasonal flooding all of which have disrupted the production patterns across the region (FAO, 1998; Forum for Livelihoods Analysis, 2005). This paper will show that the livelihoods of most of the population of South Sudan revolve around livestock raised in rangelands. It will further address some of the challenges affecting the livestock industry with a view to developing areas and opportunities on which informed decisions on policy and strategy could be made as affected by livestock and rangelands interactions. Nature of rangelands Rangelands are areas, which by reason of low and erratic precipitation, rough topography, fragile soils and poor drainage, are unsuitable for cropping but are a source of forage for free ranging wild and domestic animals as well as a source of forest products such as wood and wild foods. They consist of natural grassland, bush and woodland. Rangelands provide environmental amenities such as scenery and open space and are increasingly being used for various recreational pursuits such as game viewing and trophy hunting. The vegetation in the South Sudan rangelands is savanna grassland dominated with acacia trees in the low rainfall areas becoming lusher with high value perennial grass species and intermittent woodlands in areas with higher rainfall. These savannas surround inland floodplains, which provide animals with good dry season grazing or toich. The importance of both savannas and toich is evident in their contribution to the livelihoods of the local inhabitants and the potential significance of livestock in the economy of South Sudan. Besides sustaining a large number of cattle, the range areas also support the cultivation of various crops such as maize, sorghum, millet, cowpeas, greengrams etc. Livelihood zones Eastern Flood Plains Subsistence cropping of sorghum and maize, and an enormous dependence on cattle keeping are the main characteristics of this zone. Ethnically, the zone is inhabited by the Murle, Jie, Nuer and Dinka who also fish and gather wildfoods such as forest fruits, leaves, seeds and nuts, mushrooms, honey etc. Green Belt This zone consists of Western and parts of Central Equatoria States and receives good rains that reach 1800 mm per annum (FAO, 1998). It is inhabited by farming communities who grow a variety of crops including sorghum, maize, cassava, groundnuts and simsim over two growing seasons. The Green Belt is tsetse fly infested and so is unsuitable for livestock except for small populations of sheep and goats. The communities (Kakwa, Moru, Zande etc.) who live here are sedentary and engage in nonlivestock trade that extends internally from Yei to Juba and Bahr el Ghazel and internationally to Congo, Uganda and Central African Republic. The Green Belt enjoyed relatively high levels of security until recent incursions and raids by the Lords Resistance Army (LRA) and inter-ethnic conflicts around Yambio. 2 Hills and Mountains Eastern Equatoria mainly represents this zone. The Taposa, Latuko, Acholi and other communities who live here, keep livestock and are generally sedentary moving only to nearby grazing areas in the dry season. They farm a variety of crops over two seasons in some areas of the zone. Ironstone Plateau This zone extends from Terekeka northwards up to the Cueibet/Tonj and Wau areas. Communities (Mundari, Dinka etc.) who keep primarily small ruminants inhabit the Ironstone Plateau. The predominant crops grown in the area include sorghum, cassava, groundnuts and simsim. Nile Sobat Corridor Abundant resources along the Nile and Sobat rivers have supported communities that fish, keep cattle and farm crops, predominantly sorghum, in this zone. The inhabitants (Nuer, Dinka etc.) enjoy a wide variety of foods and sufficient water throughout the year from its rivers and swamps. Good rains often result in flooding of low-lying farms particularly in the swamps of Bor, Zeraf and Panyinjar and ensure access to fish, wild foods and ratoon crops. Western Flood Plains Livestock keeping communities who also grow sorghum, groundnuts, simsim and maize occupy the Western Flood Plains of greater Bahr el Ghazel. The gathering of wild foods and fishing are important activities and sources of food in this zone. There is interregional trade for surpluses from Gogrial, Tonj, Rumbek and Wau into communities in North Sudan. Major livestock communities Livestock is key to food security and to the social and economic well being of about 80% (FEWS, 2006) of the population of South Sudan. Cately et al. (2005) have categorised the main livestock communities into pastoralists and agropastoralists although evidence from the livelihoods patterns above would describe all livestock keepers as agropastoralists. The relatively dry and lowland areas of Eastern Equatoria is inhabited by Taposa, Jie, Murle and Nyangatom agropastoralists while the Mundari, Dinka and Nuer live in the flood plains around the Nile tributaries and in what is popularly known as the Nile Corridor which is the area surrounding the Nile, Sobat, Pibor and Zeraf rivers. Smaller numbers of livestock are also kept in the hills and mountain zone east of the Nile in Equatoria (Cately et al., 2005). Cattle, sheep, goats and donkeys are the major species in the livestock rearing areas; the introduction of camels into Eastern Equatoria in the early sixties was deemed unsustainable. Milk and meat constitute 30, 40 and 65% of the diet in 3 a normal year food economy for the Dinka, Nuer and Taposa respectively (Fielding et al., 2000). The Taposa cherish blood with their meat and do not eat fish but similar to the other ethnic communities they also consume wild foods and crops. Production Systems Rainfall in the livestock producing areas is variable, rarely exceeds 850 mm per annum (FAO, 1998) and is similar to precipitation in the rangelands of Kenya (see Abate et al., 1995). The rain is sufficient to support grass species of the genera Agrostis, Panicum, Cenchrus, Echnicloa, Andropogan, Brachiaria, Sporobola, Chloris, Sorghum and Hyparrhenia associated with browse species of Acacia, Balonites, Indigofera, Leucaena and Carica (Elis, 1982). The nutritive value of some these species given in Table 1 show them to contain high levels of essential nutrients and energy. Table 1: Chemical composition (g kg-1 DM) and energy value (MJ kg-1 DM) of grass and browse species native to South Sudan rangelands1 Species CP CF Ca P ME Cenchrus ciliaris Panicum maximum Pennisetum purpureum Chloris gayana Sorghum arundinaceum Hyparrhenia rufa Acacia albida fruit Acacia tortilis leaves Balonites aegyptiaca leaves Leucaena leucocephala leaves 56.1 97.2 77.9 81.3 67.3 42.0 109.0 128.4 116.5 488.0 433.5 334.8 456.1 504.5 376.5 202.5 105.0 164.0 3.8 4.1 4.0 3.9 4.9 2.63 38.5 4.8 1.5 1.7 2.1 1.9 2.9 1.5 2.2 0.5 8.32 9.36 7.68 8.48 8.32 9.04 11.80 11.94 11.20 218.6 200.5 5.6 3.2 11.52 1 After Elis (1982) - indicates values not available For the Toposa, Murle, Jie and Nyangatom, the production system is defined by transhumant movement of animals and people from permanent, wet season homesteads in search of water and grazing. Similarly, in the flood plains of the north and west, Nuer and Dinka herders move their animals to nutritionally high dry season grazing or toich when flood waters recede and return them to higher ground when the rains begin. Only in the dry season when tsetse populations have fallen can cattle graze in the hills and mountain zone; with the onset of rains, tsetse numbers build up forcing herds back to the lowlands 4 (Cately et al., 2005). These movements notwithstanding, breeding of cattle among the livestock keepers is timed so that calving coincides with periods of pasture availability. It is estimated that the transhumant agropastoralist production system sustains between 5 and 8 million cattle (Jones, 2001; WFP, 2004) in the rangelands of South Sudan. Besides providing food, manure and hides and skins, South Sudanese livestock is often sold or exchanged for grain. Over the years, markets have emerged and thrived albeit under constrained conditions particularly of security. Internal and external trade in cattle have been summarised from the reports of the Forum for Livelihoods Analysis (2005) and Cately et al. (2005) viz: In the Eastern Flood Plains militia activity in this zone limited market activity into Bentiu, Malakal and Nasir. Similalry, LRA activity constrained movement within the Hills and Mountains zone and restricted trading from Eastern Equatoria to Juba and internationally with Uganda and Kenya. Walking animals from Bahr el Ghazel through Yei to northern Uganda was a major trading route as was the walking of Toposa animals to Narus before trucking through Lokichokio to Nairobi for slaughter. Small numbers of animals would also be walked from the Sobat Basin into Malakal and Ethiopia. Internally, an improved security situation in the Nile Sobat Corridor has resulted in increased movement and rural-urban trade along the Leer-Bentiu road and by river into Malakal. There is high potential for cattle rustling in the Ironstone Plateau zone because of increasing cattle prices and increased sales into towns. In the Western Flood Plains, there is inter-regional trade for surplus animals from Gogrial, Tonj, Rumbek and Wau into communities in North Sudan. The incidence of disease among South Sudanese cattle was high before the introduction of community based animal health service by UNICEF-OLS in 1993. Rinderpest is now under control although other epidemic diseases still affect South Sudan livestock. Nagana is a common cattle disease in Western Equatoria while small ruminants die often from liver flukes, mange and worms. Foot and mouth disease reduce production in adult cattle and cause calf deaths; CBPP is endemic and ECF is emerging as an important disease in Equatoria and Jongolei (Cately et al., 2005). Challenges to production and measures for improvement Due to lack of quantitative data the influence of quantity and quality of available herbage on animal productivity will not be considered here. Neither will an analysis of production factors or the effect of individual nutrients on productivity be undertaken. Only the environmental effects of an extensive grazing system on range resources will be dealt with instead in order to suggest those institutional measures that are conducive to sustainability of the range. Understanding the agropastoralist system The agropastoralist system has evolved over time and is run by a complex cultural and social organisation whose strategies and needs are little understood by those outside the 5 system. The starting point, therefore, is to understand the variability and diversity that exists in the agropastoralist areas in order to find sustainable solutions for management of the system. In this regard, it is well to stress community participation in the planning and implementation of common-property programmes and in ensuring adequate preparedness and response in the face of calamities such as drought or flooding. In Namibia, Mufune (2004) showed that a community owned and driven livestock project contributed to poverty reduction in rural areas because the community felt empowered and made decisions that benefited members. Water resources and their management Regular and adequate supply of water to livestock is essential for their existence and sustenance of productive functions. Available evidence indicates that water availability is a problem in the lowlands of Eastern Equatoria particularly in the dry season. In the flood plains, seasonal movement to toich ensures adequate water supply for Mundari, Dinka and Nuer herds and flocks. Be as it may, it is still desirable that a policy on development of water points be looked into as experiences in Kenya (Abate et al., 1995) and Namibia (Abate, 2004) have shown lowered animal outputs from the range when water supply points are absent, few or far apart. Limited water resources always lead to high grazing pressures around permanent water points resulting in deterioration of the range. It is, therefore, important to consider the building of earth dams, construction of wells, deepening of water catchment areas and sinking of boreholes to facilitate accessibility to water. Such a strategy would ensure controlled grazing of feed resources, enable more areas to be grazed, allow conservation of dry season grazing and reduce feed requirements for trekking (Abate et al., 1995). To ensure continuity of their useful existence and enhancement of their social acceptability, the management of the water resources need to be vested in the communities. Multiple species grazing It is accepted that the best way of utilizing range resources efficiently is in keeping a diverse herd of animals. This is presently the practice in the South Sudanese rangelands and although the proportions of the different livestock species have not been quantified, an appropriate balance need to be promoted thorough the extension service. Comparative studies on feeding behaviour of ruminants and camels have shown them to be complementary rather than competitive. Schwartz (1987), working in northern Kenya, reported that mixed species herds increase food production, minimise risks in pastoral use systems and are less detrimental to range condition and productivity than animal monocultures. Thus, with a multiple species grazing system, the South Sudanese range would support more livestock numbers than is currently the case without damaging the environment. 6 High stock numbers lead to environmental degradation The South Sudanese range environment can only be sustained if stocking rates are matched to the carrying capacity of the rangelands. As has been shown elsewhere in subSaharan Africa (ILCA, 1986/87) areas with high livestock densities are always overgrazed of palatable grasses and shrubs leaving behind less palatable species that become prominent under drought and can barely meet the maintenance and reproduction requirements of livestock. Thus, it is instructive for livestock keepers to consistently cull and sell unproductive animals such as infertile females and old castrated males using the well established system of livestock auctions in order to ensure that the range holds manageable numbers of animals. The return to normalcy of major towns in South Sudan could provide internal markets for livestock producers (Cately et al., 2005). And, as indicated in earlier paragraphs, there are already livestock trade opportunities with Uganda, Kenya, the Democratic Republic of the Congo and North Sudan, which need to be formalised through investment in infrastructure, trade agreements and enabling policies. Improvements to the feed resource base Because of erratic rainfalls, shortages of available pasture are frequent and a major constraint to livestock production in the southern Sudanese lowlands. An afforestation programme involving local people should therefore be considered. The planting of high fodder yielding indigenous trees and shrubs can increase the dry matter output of the range and improve the vegetation offtake from it by livestock. The agropastoralists in collaboration with forest and range specialists need to identify promising plants for inclusion in grazing areas. It is relevant here to report the work of Kassilly and Abate (2002), which showed that Euphorbia spp. a planted genus, was the most preferred in the diet selected by camels in the Baringo district of Kenya. In the long term, shrubs and trees are a least cost alternative. Moreover, according to Kayongo-Male (1986), herbs, dwarf shrubs, tree leaves and litter constitute the major portion of cattle diets in the dry season. Leguminous trees are, particularly, useful because they add to soil fertility. Rothauge et al. (2003) observed preference by cattle for grasses growing under leguminous trees because of soil enrichment caused by the tree that eventually improved the nutritive value of the sub-canopy grasses. Indeed forests and forest products, many of which are used by the agropastoralist, should be considered in the decision making processes relating to South Sudan resources management. Grazing management The range environment risks being destroyed unless grazing is managed efficiently. As with the water points, the different livestock communities need to be entrusted with managing this important resource. They would be required to define time and areas to be grazed throughout the year, monitor range condition and agree on de-stocking through sales. These measures should be additional to the traditional methods of deferred grazing 7 and conservation. The success of a community management strategy would require confidence building among the different communities so as to stamp out cattle raiding for restocking purposes and inter-ethnic conflicts, which, currently are quite frequent, and affect access to grazing areas. Government would then be required to compliment community efforts by investing in resource mapping and early warning systems which knowledge could be used in designing livestock movements for efficient and sustainable utilization of the range. The Livestock Early Warning System (LEWS) is already being used to monitor livestock and foliage conditions in Kenya, Somalia and Ethiopia (FEWS, 2006) Disease control The disease environment is considered here in the context of increasing productivity from the range so as to make investing in its sustainability worthwhile. Again the use of indigenous knowledge to control disease is to be encouraged. Otherwise, strategic mass vaccinations against common diseases and use of anthelmintics would greatly increase survival rates. Benefits from vaccinations will be enormous viewed against the almost daily reporting of rinderpest occurrence by community animal health workers in 1993 (see Cately et al., 2005). Indeed, persistent large scale use of rinderpest vaccine has made cattle production profitable in many parts of sub-Saharan Africa. Routine vaccinations and deworming should be coupled with periodical cost-effective herd health programmes for early detection and treatment of disease. Role of research Problem solving and multisector research that encourages from-below analysis is to be encouraged in order to sustain the range and make it more productive. Monitoring of resource trends using suitable indicators is desirable to prevent land degradation. Research into the agropastoral way of life will result in the evolution of institutions and mechanisms that can assist with conflict resolution among communities. Continuous research into markets, market access and product pricing will ensure that livestock in the rangelands remain an economic asset. References Abate, A.L. (2004). Briefing paper: Livestock, animal health and range management. Northern Regions Livestock Development Project (NOLIDEP): Ministry of Agriculture, Water and Rural Development, Namibia. 30 pp. Abate, A., Wakhungu, J.W. and Said, A.N. (1995). Cattle, goats, sheep and camel production on range: the Kenya experience. Bull. Anim. Hlth. Prod. Afr., 43:145-156 8 Cately, A., Leyland, T. and Bishop, S. 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Review of rinderpest control in Southern Sudan, 1989-2000. AU/IBAR, Nairobi, Kenya Kassily, F.N., and Abate, A.L. (2002). Composition and quality of camel diets in central Baringo, Kenya. Bull. Anim. Hlth. Prod. Afr., 48:239-247 Kayongo-Male, H. (1986). Feeding habits, forage quality and food intake by zebu cattle grazing natural rangelands in the IPAL study area. IPAL Technical Report E8, Unesco, Nairobi, Kenya Mufune, P. (2004). Briefing paper: Poverty and social aspects. Northern Regions Livestock Development Project (NOLIDEP): Ministry of Agriculture, Water and Rural Development, Namibia. 52 pp. Rothauge, A., Smit, G.N. and Abate, A.L. (2003). The effect of the sub-habitat below savanna trees on soil, grass and its utilization by cattle. Proceedings of the VIIth International Rangelands Congress, 26th July-1st August 2003, Durban, South Africa. pp. 106-109 Schwartz, H.J. (1987). 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