T.Gitau,J.J.McDermott2,3,D. Waltner-Toews3,J.M. Gathuma1, E.K.Kang1, V.W.Kimani4, J.K.Kilungo5, R.K. Muni6, J.M. Mwangi1 and G.O. Otieno7
Department of Public Health, University of Nairobi, Nairobi, Kenya
International Livestock Research Institute, Nairobi, Kenya
Department of Population Medicine, University of Guelph, Guelph, Canada
Pest Control Products Board, Nairobi, Kenya
Department of Agricultural Economics, University of Nairobi, Nairobi, Kenya
Department of Agricultural Engineering, University of Nairobi, Nairobi, Kenya
Institute of African Studies, University of Nairobi, Nairobi, Kenya
The paper briefly describes the application of agro-ecosystem health framework for characterisation of an agro-ecosystem in central Kenya, and identification of the indications of its health. The lessons learnt from the application are briefly discussed.
Given the newness of the agro-ecosystem health (AESH) field, the major accomplishments to date are conceptual and methodological. The empirical information that exists serves, for the most part, to demonstrate the applicability of the concept rather than supply a comprehensive numerical estimate of the health status (Smit et al 1998) of a given ecosystem. The University of Nairobi and the University of Guelph are carrying out a research programme (funded by International Development Research Centre, IDRC) whose objective is an integrated assessment of a tropical highland agro-ecosystem using the agro-ecosystem health framework.
This approach acknowledges that an agro-ecosystem can be defined from many different perspectives, giving rise to multiple—conflicting or complementing—descriptions of them. Considering all these perspectives is the only means to elucidating the structural-functional characteristics of the agro-ecosystem. Stakeholders must therefore be included in both the definition of the system and in its description. For the system to be sustainable, the stakeholders must be part of the search for solutions. Their involvement in problem identification, analysis, planning and implementation becomes a key component of the process. Indeed, they must own—and feel that they own—the problems, the solutions and the means of solving them.
To incorporate these concerns, this project is using participatory techniques, soft system methodologies and conventional research methods in an integrated, iterative and trans-disciplinary process that both evaluates and attempts to improve the health of agro-ecosystems. The process involves: (1) characterisation of the agro-ecosystems, (2) development of health indicators, (3) empirical assessment of indicators (monitoring and evaluation), and (4) taking remedial action where pathologies are detected.
This paper describes the methods used in the characterisation of the agro-ecosystem and selection of indicators. The lessons learnt from the application of these techniques are briefly discussed.
The study is being carried out in Kiambu District, Kenya. The district is divided into several hierarchical administrative zones (Figure 1). The three lowest levels of the agricultural hierarchy (the village, farm and field) are being targeted. Six villages were selected through a multi-stage but purposive sampling strategy. The key factors influencing selection of a village were preponderance of farmers and presence of other research and development agencies. Data on villages (names of villages, their boundaries, farming activities, development activities) was supplied by opinion-leaders from the locations.
Figure 1. Hierarchy in agro-ecosystems: The central highlands of Kenya.
A five- to eight-day participatory action research (PAR) workshop was held in each of the six villages. Community members were informed about the workshop through opinion leaders, churches, administration officials (Chiefs and Assistant Chiefs) and posters. The workshops were held in venues within the village. Workshops commenced with an explanation of purpose and seeking community acceptance of the exercise. Communities were allowed to set their own time-schedules and to prepare budgets for refreshments, foods and other expendables required during the exercise even though the funds were provided by the AESH project. This served as a trend-setting mechanism for participation. Table 1 shows the key PAR techniques, the expected outputs and the order in which they were used.
Soft systems methodology (SSM) is an approach to studying human activity systems developed by management specialists (Checkland and Scholes 1990). The methodology includes rich descriptions of problematic situations and the creation of various systems models, as well as an exploration of the social and cultural context for the systems being considered.
Cultural and social settings within the various human activity sub-systems in the village were studied. Relationships between various interest groups and stakeholders in the village were assessed through discussions with people involved and depicted in rich pictures. A similar approach was used to analyse the meaning ascribed to various social, cultural and economic issues in the village. Roles, norms and values ascribed to various stakeholders in the village were examined. Note was taken as to what embodies opinion leadership in the village and how leadership positions are obtained, used and protected. Root definitions, which are used in SSM to describe the actors and beneficiaries, the world-views on which their models are based, and the environmental constraints of the systems, were used to model both the primary-task and the issue based sub-systems in village agro-ecosystems.
Semi-structured interviews were conducted during the transect walks of the PAR workshops. Communities were asked to stratify farms and/or households in the village based on criteria developed in a participatory manner. Households to be interviewed were selected from each stratum based on a random process but taking into consideration the availability of household members for the interview. A team of three people visited each of the selected households: a researcher, an extension agent, and one community member. The household head was requested to give a guided tour of the farm/dwelling. Farm sketches were made indicating types of enterprises and resource availability and utilisation. The interview was administered following a checklist (Table 2). Copies of farm records were made as well as a listing of time and work schedules.
Table 1. PAR tools used in the study and the expected outputs.
|
|
Objectives |
Tools |
Expected
output |
|
1. |
Introduction |
Self
introduction, pairing, speeches, ice-breakers |
Acceptance/permission
to carry out exercise |
|
2. |
Planning
for the workshop |
Time
schedules, assigning roles and responsibilities |
Workshop
logistics, trend-setting for community participation |
|
3. |
Village
boundaries and inventory
of resources |
Social
map |
Location
of farms and households, names and sex of HH heads, boundaries |
|
|
|
Resource
map |
Inventory
of resources, infrastructure, state of resources, identify problems |
|
4. |
Historical
background |
Historical
profile |
Community
identity and history, past events and their impacts, coping strategies |
|
5. |
Trend-lines
and time-lines |
Trend
charts |
Lists
changes, direction of change, triangulation of (4) above |
|
6. |
Seasonal
trends |
Seasonal
calendars |
Seasonal
trends in climate, economic and social activities |
|
7. |
Transect
walks |
Route
mapping |
Identification
of issues and problems |
|
Walk |
Observation
of type and status of resources, problem identification, triangulation |
||
|
Transect
profile |
Resource
inventory |
||
|
Semi-structured
interviews |
Observation
of type and status of resources, problem identification, triangulation |
||
|
8. |
Resource
mobility |
Mobility
charts |
Flow
of goods, services and resources to and from village |
|
9. |
Identification
and analysis of institutions |
Venn
(chapati) diagrams |
Types,
numbers and importance of institutions, problem identification |
|
10. |
Major
gender concerns |
Activity
profile |
Types
and degree of drudgery of chores, persons responsible |
|
Daily
calendar |
Daily
routines by age and gender |
||
|
Access
and control matrix |
Resource
types, ownership, control and
utilisation by age and gender |
||
|
Decision
making matrix |
Power
and opinion leadership issues in the village and household |
||
|
11. |
Major
health concerns |
Health
analysis |
Types,
causes and importance of major health concerns by age and gender |
|
12. |
Problem
identification and analysis |
Problem
listing |
Triangulation
of needs |
|
Ranking
(pairwise/matrix) |
List
of needs in order of priority |
||
|
Problem
analysis |
Opportunities
and constraints, coping strategies, possible solutions |
||
|
13. |
Action
planning |
Community-action
planning |
Resources,
schedules, strategies |
In addition, a survey of all households in the village was conducted. The survey questionnaire was designed in the local language. Information on household structure, farm/household management, incomes, farm productivity and resource availability/ utilisation was sought. The village ecosystem committee members were trained to assist households in filling-in the forms to ensure a high response rate.
Gitau (1997) provides a detailed description of biophysical, socio-cultural and economic characteristics of the Kiambu AES. From this a summary of goals, objectives, expectations, problems and issues of concern of stakeholders in the Kiambu AES was developed. Influence diagrams with linkages between various issues and problems as visualised by the communities were drawn. From these, a generalised list of attributes relating to issues, goals, objectives and expectations of the main stakeholders in the AES were derived. Variables that reflect changes in these attributes over the short- (fast changing = current to one year), medium- (between one and three years) and long-term (more than three years) were listed. Indicators were selected from these variables based on their validity, feasibility and who the operator and/or end-user would be. Variables selected as indicators were those having a high feasibility (practicality of measurement, cost/time effectiveness) and validity (how well it measures the attribute of concern). Some attributes are of interest to a variety of groups (researchers, farmers, community in general, policy makers etc). Indicators for these attributes were selected based on the ease of measurement and interpretation by the users.
Methods of analysis and synthesis for data generated by AESH research are still being explored. Several complex-systems approaches—ranging from influence diagrams and loop models to various forms of catastrophe and chaos theory—seem to be promising. The loop models seem to be the most transparent in terms of understanding internal system dynamics. Figure 2 shows an interim conceptual model of the AES. Outputs are divided into amenities, by-products and value products. The external environment and the human activity system influence the type, quality and quantity of output through subsidy to the system (Izac and Swift 1994). The external environment and the human activity system influence the type, quality and quantity of output through subsidy to the system. With time, more detailed models will be used to study system behaviour in terms of various ecosystem health attributes (and hence indicators). System characteristics such as integrity, adaptability, efficiency, effectiveness, resilience, productivity, stability and equity will be varied in order to predict system behaviour under various conditions. Values taken by attributes under these conditions will be taken as reflecting system thresholds, targets and ranges.
Table 2. Checklist for the semi-structured interview.
|
1. |
Introduction Introduction Personal Data Name of household head HH size Occupation |
8. |
Access and control Ownership of resources Decision making Utilisation of proceeds Activity profile |
|
2. |
Land use Settlement history Acreage Ownership/Tenure Access to control of land Apportionment of land |
9. |
Water Sources Uses |
|
3. |
Crop production Types of crops Cropping seasons Crop rotation Soil conservation measures |
10. |
Institutions Types of institutions Relative importance Membership Activities and responsibilities Benefits derived Family ties, friends, neighbours |
|
4. |
Agroforestry Types of trees and their uses Trends in vegetation cover |
11. |
Human health Common diseases Health of the household members Trends in disease occurrence |
|
5. |
Livestock production Species of livestock and breeds Relative importance Pests and diseases of livestock |
12. |
Off-farm income generating activities Types Relative importance Schedule of activities |
|
6. |
Yields and outputs Types of farm produce Marketing of produce Trend and seasonality of prices |
13. |
Problems and coping strategies Soil fertility Pests and crop diseases Livestock diseases Markets and prices Costs and availability of inputs Water quality and availability Usefulness or lack of institutions |
|
7. |
Farm inputs Fertiliser Concentrates and supplements Fodder Seeds Labour Vet. services Availability of credit |
|
|
Figure 2. A simplified conceptual model of the agro-ecosystem.
Agro-ecosystem health studies are currently underway in several other countries as well as Kenya. These have demonstrated that holistic approaches—such as agro-ecosystem health—are feasible even under difficult field conditions.
In some ways the current study is a revisiting of older notions of integrated community development, but with more explicit consideration of both systems theories and the socio-economic, political and ecological dimensions which are the determinants of agro-ecosystem health. It takes cognisance of the multiplicity of perspectives and interests. The SSM approach facilitates an understanding of conflicts, opinion leadership and the power structure within the human activity sub-systems. This provides a more structured system for dealing with equity and development issues than standard community development approaches.
The combination of participatory work and systems theories grounds the work both theoretically and practically, providing a framework through which health and sustainability can be promoted. It circumvents the basic problem with standard research and development programmes: the inability to arouse popular participation (Holdcroft 1984) while providing a means—to communities, researchers and policy makers—for monitoring and evaluating both the human activity and the underlying biophysical sub-systems.
The key constraints within the agro-ecosystem health approach are the difficulty in bridging the interdisciplinary gap and the potential resistance to the empowerment of disadvantaged (but not always the minority) groups within the multiplicity of stakeholders in the system. The approach is potentially disruptive to existing power-structures because of its all-inclusive, empowering-through-information approach. Moreover, methods for a more holistic interpretation of empirical data (both qualitative and quantitative) are yet to be developed. However, the incorporation of a plurality of approaches and ideas ensures that the learning cycle remains open.
Checkland P. and Scholes J. 1990. Soft systems methodology in action. John Wiley & Sons, Chinchester, England, UK.
Gitau T. 1997. Report of participatory action research workshops held in six villages of Kiambu District. Department of Public Health, University of Nairobi, Kenya (Mimeo).
Holdcroft L.E. 1984. The rise and fall of community development, 195065: A critical assessment. In: Eicher C. and Staatz J. (eds), Agricultural development in the third world. The John Hopkins University Press, London, UK. pp. 4658.
Izac A. and Swift M.J. 1994. On agricultural sustainability and its measurement in small-scale farming in sub-Saharan Africa. Ecological economics 11:105125.
Smit B., Waltner-Toews D., Rapport D., Wall E., Wichert D., Gwyn E. and Wandel J. 1998. Agro-ecosystem health: Analysis and assessment. Faculty of Environmental Science, University of Guelph, Guelph, Ontario, Canada. 114 pp.