![]() | The Improvement of Tropical and Subtropical Rangelands (BOSTID) |
![]() | ![]() | (introduction...) |
![]() | ![]() | Acknowledgements |
![]() | ![]() | Panel on the improvement of tropical and subtropical rangelands |
![]() | ![]() | Contributors |
![]() | ![]() | National research council staff |
![]() | ![]() | Preface |
![]() | ![]() | Overview: Dimensions of a worldwide environmental crisis |
![]() | ![]() | The geographical scope |
![]() | ![]() | References |
![]() | ![]() | Part I |
![]() | ![]() | Introduction |
![]() | ![]() | (introduction...) |
![]() | ![]() | References |
![]() | ![]() | The nature of tropical and subtropical rangelands |
![]() | ![]() | (introduction...) |
![]() | ![]() | Range classification |
![]() | ![]() | Social system-ecosystem interactions |
![]() | ![]() | References |
![]() | ![]() | The social context for rangeland improvement |
![]() | ![]() | (introduction...) |
![]() | ![]() | Production systems in tropical and subtropical regions |
![]() | ![]() | Context of environmental degradation |
![]() | ![]() | References |
![]() | ![]() | The economic context |
![]() | ![]() | (introduction...) |
![]() | ![]() | Range systems |
![]() | ![]() | The basis of range economics |
![]() | ![]() | Project analysis |
![]() | ![]() | Determining costs and benefits |
![]() | ![]() | Resource evaluation |
![]() | ![]() | Market price determination |
![]() | ![]() | References |
![]() | ![]() | Regional resource assessment |
![]() | ![]() | (introduction...) |
![]() | ![]() | Information needs |
![]() | ![]() | Information acquisition |
![]() | ![]() | References |
![]() | ![]() | Site evaluation |
![]() | ![]() | (introduction...) |
![]() | ![]() | An ecosystem perspective |
![]() | ![]() | A systems approach to site evaluation |
![]() | ![]() | Evaluation of abiotic and biotic components |
![]() | ![]() | Integrated evaluations |
![]() | ![]() | References |
![]() | ![]() | Grazing management |
![]() | ![]() | (introduction...) |
![]() | ![]() | Grazing management concepts |
![]() | ![]() | Time of grazing |
![]() | ![]() | Distribution of grazing |
![]() | ![]() | Type of animal grazing |
![]() | ![]() | Number of animals grazing |
![]() | ![]() | Grazing management planning |
![]() | ![]() | Grazing management systems |
![]() | ![]() | Livestock management |
![]() | ![]() | The herima system in Mali |
![]() | ![]() | References |
![]() | ![]() | Rehabilitation techniques |
![]() | ![]() | Establishing plants on the range |
![]() | ![]() | Natural revegetation |
![]() | ![]() | Direct seeding |
![]() | ![]() | Improvement of tropical and subtropical rangelands |
![]() | ![]() | Selected practices |
![]() | ![]() | References |
![]() | ![]() | Criteria for plant selection |
![]() | ![]() | Project planning |
![]() | ![]() | Socioeconomic and management considerations in feasibility studies |
![]() | ![]() | Adaptation to ecoclimatic conditions |
![]() | ![]() | Adaptation to soils |
![]() | ![]() | Adaptation to physiography, geomorphology, topography, slope, and aspect |
![]() | ![]() | Ability of introduced species to compete with native vegetation |
![]() | ![]() | Use regimes |
![]() | ![]() | Availability of seeds and plant materials |
![]() | ![]() | Maintenance of biological diversity |
![]() | ![]() | Plant improvement |
![]() | ![]() | References |
![]() | ![]() | Part II |
![]() | ![]() | Introduction to the case studies |
![]() | ![]() | Pastoral regimes of Mauritania |
![]() | ![]() | (introduction...) |
![]() | ![]() | Physical geography |
![]() | ![]() | Migration cycle |
![]() | ![]() | The Beni Mguild of Morocco |
![]() | ![]() | (introduction...) |
![]() | ![]() | Physical geography |
![]() | ![]() | Migratory cycle |
![]() | ![]() | The Kel Tamasheq |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Camp organization |
![]() | ![]() | References |
![]() | ![]() | Dromedary pastoralism in Africa and Arabia |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Reproduction and risk |
![]() | ![]() | Management and labor |
![]() | ![]() | Subsistence production |
![]() | ![]() | Marketing |
![]() | ![]() | Predatory pastoralism |
![]() | ![]() | The future of camel pastoralism |
![]() | ![]() | References |
![]() | ![]() | The mountain nomads of Iran: Basseri and Bakhtiari |
![]() | ![]() | (introduction...) |
![]() | ![]() | The physical environment |
![]() | ![]() | The basseri |
![]() | ![]() | The bakhtiari |
![]() | ![]() | The Marri Baluch of Pakistan |
![]() | ![]() | (introduction...) |
![]() | ![]() | Physical environment |
![]() | ![]() | Seasons and migrations |
![]() | ![]() | A mixed economic system |
![]() | ![]() | Conclusiones |
![]() | ![]() | Changing patterns of resource use in the Bedthi-Aghanashini valleys of Karnataka state, India |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | The setting |
![]() | ![]() | Human communities |
![]() | ![]() | Traditional patterns of resource management |
![]() | ![]() | Colonial period |
![]() | ![]() | After independence |
![]() | ![]() | Recent trends |
![]() | ![]() | References |
![]() | ![]() | Kenya: Seeking remedies for desert encroachment |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Background |
![]() | ![]() | Traditional pastoralism |
![]() | ![]() | Baseline studies |
![]() | ![]() | Vegetation and livestock |
![]() | ![]() | Directions for the future |
![]() | ![]() | The hema system in the Arabian peninsula |
![]() | ![]() | (introduction...) |
![]() | ![]() | Rights of ownership or use |
![]() | ![]() | The hema system in Saudi Arabia |
![]() | ![]() | The mahmia or marah, and the koze system in Syria |
![]() | ![]() | Neglect of the hema and its consequences |
![]() | ![]() | Hema in the range improvement and conservation programs in the near east |
![]() | ![]() | References |
![]() | ![]() | Wildlife land use at the Athi River, Kenya |
![]() | ![]() | (introduction...) |
![]() | ![]() | Background |
![]() | ![]() | Some early findings |
![]() | ![]() | Conclusion |
![]() | ![]() | Camel husbandry in Kenya: Increasing the productivity of ranchland |
![]() | ![]() | (introduction...) |
![]() | ![]() | Introduction |
![]() | ![]() | Location |
![]() | ![]() | Vegetation |
![]() | ![]() | Livestock |
![]() | ![]() | Introduction of camels |
![]() | ![]() | Management and adaptability |
![]() | ![]() | Reproduction and lactation |
![]() | ![]() | Veterinary notes |
![]() | ![]() | Economics |
![]() | ![]() | Reference |
![]() | ![]() | The potential of faidherbia albida for desertification control and increased productivity in Chad |
![]() | ![]() | (introduction...) |
![]() | ![]() | Background |
![]() | ![]() | Characteristics of faidherbia albida |
![]() | ![]() | Project description |
![]() | ![]() | Project analysis and evaluation |
![]() | ![]() | Conclusions |
![]() | ![]() | References |
![]() | ![]() | Improving Nigeria's animal feed resources: Pastoralists and scientists cooperate in fodder bank research |
![]() | ![]() | Board on science technology for international development |
![]() | ![]() | (introduction...) |
![]() | ![]() | Members |
Evaluating the quality and adequacy of various resources for possible alternative uses is the first step in project planning. The climate and characteristics of land and soils, water supply (whether for irrigation, livestock, or domestic use), and incidence of weedy types of vegetation, insect pests, and plant or animal diseases should all be considered. The objectives of the evaluation process are to determine the forage and livestock enterprises that may be feasible and whether some alternatives can be ruled infeasible without further evaluation. These factors are described in more detail in chapters 4 and 5.
Location of the project and access to markets both for sale of products and for purchase of necessary supplies is another key consideration for determining feasibility. The location, climate, land, and water supply factors are often fixed. It is impossible, or at least difficult and often costly, to modify these factors. Water supply can sometimes be augmented by drilling wells or creating storage; however, the ecological consequences must be considered.
Human resources are the most difficult to assess. Most projects rely on organizations of pastoralists. Important questions to address are the following: Will the existing organizations be used, or will a new organization be established? What should be the size of the organization? How complex will be the functional specialization and what type of membership (inclusive versus exclusive, voluntary versus forced) is expected?
A new organization can only be established at a cost. Because of low population densities associated with arid rangeland, communication between members is difficult. Difficulties in decision making, therefore, increase as group size increases. For the same reason (lack of opportunity to communicate), there are limits to functional specialization.
Sanford (1983) emphasizes that the "costs" of project organization are often underestimated if not overlooked altogether. A first step to the evaluation of human resources is a good understanding of the existing social organization.
Data Needs and Sources
Data required for cost and benefit evaluation, frequently called "input-output" data, include: herbage or animal production or possible alternatives; physical quantities of inputs used, whether a product is produced or purchased; prices for inputs; and prices for output to be sold.
The principal sources of physical input-output data for projects may include well-trained professionals with technical expertise in the area, data from other projects of a similar type and under similar conditions, people from the locality with good knowledge of the area and what might be expected, and data from controlled experiments.
Preliminary experiments are very important sources of data for technical specialists who must make judgments about the productivity of resources in new projects. The preliminary experiments do not yield perfect or reproducible results, particularly when applied to international projects of an agricultural nature where factors such as weather, variability in inputs, and the performance of the field crew typically are incompletely controlled. Situations in developing countries lead to what might be called the experimental gap" between the yields that are obtained on the experimental plots and those likely to be achieved on projects. The technical specialists must attempt to estimate the extent of experimental gap and the extent of adjustment or correction. Farming systems research is attempting to narrow this gap.
In general, local data are most useful for ascertaining the response to different treatments or the change in output resulting from a change in level of the inputs.
Farmers or pastoralists may be the best source of information on crop or vegetation and animal performance, requirements for labor, materials, machinery use, feed requirements, and so on. Information collected locally by survey procedures can be used to establish benchmarks for current enterprise combinations and production practices, and to obtain crop and livestock labor requirements and machine use levels for operations of different sizes.