ReviewConservation agriculture and smallholder farming in Africa: The heretics’ view
Introduction
Conservation agriculture (CA) is proposed as a panacea to agricultural problems in smallholder farming systems in the tropics (Hebblethwaite et al., 1996, Steiner et al., 1998, Fowler and Rockström, 2001, Derpsch, 2003, Hobbs, 2007, Hobbs et al., 2008). It specifically aims to address the problems of soil degradation resulting from agricultural practices that deplete the organic matter and nutrient content of the soil and, moreover, it purports to address the problem of intensive labour requirements in smallholder agriculture (African Conservation Tillage Network, 2008). Proponents of CA suggest that it offers a solution to these problems by providing “the means that can prevent further destruction of precious soils, increase rainwater use efficiency and labour productivity, thereby ensuring higher and more stable yields while […] reduc[ing] production costs”. Given the continuing poor-productivity of smallholder agriculture in sub-Saharan Africa (SSA), and the alarming reports of soil degradation due to nutrient depletion and soil erosion (Stoorvogel and Smaling, 1998, Drechsel et al., 2001) CA appears to offer great potential to address these problems.
Zero-tillage was born out of a necessity to combat soil degradation and has been widely adopted by farmers of different scale in North and South America (Bolliger et al., 2006, Triplett and Warren, 2008). Brazil's “Zero-tillage revolution”, in particular, is viewed as an attractive potential solution to reversing soil degradation and increasing land productivity in SSA (Fowler and Rockström, 2001, Hobbs, 2007). Zero-tillage, together with crop residue management (mulches) and crop rotation are the pillars of CA as it is now actively promoted by a growing number of research and extension programmes, supported by major international initiatives (e.g. FAO – Benites and Ashburner, 2003, FAO, 2008a; the Direct-sowing, Mulch-based, Conservation agriculture (DMC) – systems initiative under the Global Forum on Agricultural Research (GFAR), the European Conservation Agriculture Federation (ECAF), etc.). Yet, apart from a few recent articles (Erenstein, 2002, Erenstein, 2003, Bolliger et al., 2006, Knowler and Bradshaw, 2007, Affholder et al., 2008, Lahmar, 2009), it appears that CA has escaped critical analysis. The more critical publications (Bolliger et al., 2006, Bolliger, 2007, Gowing and Palmer, 2008) address pertinent issues such as: (a) Which principles of CA, and under which conditions, actually contribute to the effects sought?; (b) What are the trade-offs of implementing CA?; (c) Does CA addresses a need identified by the farmer or one mainly identified by scientists and policymakers?; and (d) Do the preconditions for adoption by smallholder farmers exist in SSA?
In our work that addresses problems of soil fertility and productivity of smallholder farmers in SSA we often see that options for soil management that show great promise under controlled experimental conditions gain little foothold in practice (Tittonell et al., 2008). Most often this is not due to technical problems of the new options. More commonly the lack of uptake occurs because farmers are constrained in resources, such that investment in a new technology not only influences what must be done in one field, but involves trade-offs with other activities from which the farmers generate their livelihood (Benoit-Cattin et al., 1991, Scoones, 2001, Giller et al., 2006). Key resources that are constrained are land, labour at key periods during the cropping cycle, feed for livestock, manure for soil amendment, money to invest in external inputs, and lack of markets for produce.
Conservation agriculture is commonly regarded as appropriate for a wide range of smallholder conditions (FAO, 2008a, FAO, 2008b), but often this assumption goes without rigorous evaluation or detailed testing. The recent FAO (2008a) framework for action on CA states that “The plough has become the symbol of agriculture and many, including farmers, extension agents, researchers, university professors and politicians have difficulty in accepting that agriculture is possible without tillage.” We do not doubt that agriculture is possible without tillage, yet when we question whether CA is the best approach, or whether the suitability of CA in a given setting has been established, the reactions are often defensive. It seems as if we assume the role of the heretic – the heathen or unbeliever – who dares to question the doctrine of the established view.
In this article we first consider the diverse benefits and claims concerning CA to explore possible constraints that may assist us in understanding when and where CA is most likely to provide substantial benefits. Second we discuss the issue of which farmers, in which settings are likely to be able to make most use of CA approaches to assist in targeting of CA initiatives in African smallholder agriculture. In addressing these questions we aim to enrich the debate around CA and smallholder agriculture to assist in identification of ‘windows of opportunity’ in space and time to which efforts on CA could be focused.
Section snippets
Which principles of conservation agriculture contribute to the desired effects?
Conservation agriculture1
Is mulching the most sensible, efficient or profitable use of crop residues?
While benefits of CA are most directly attributed to the mulch of crop residues retained in the field, limited availability of crop residues is under many farming conditions an important constraint for adoption of CA practices. The retention of mulch is the defining aspect of CA in (sub-)tropical countries where tillage is traditionally much less intensive than in temperate countries (Erenstein, 2003). Whereas the US Conservation Technology Information Center (CTIC, 1999) defined conservation
Evidence of ‘adoption’
Confusion abounds in the literature as to what constitutes ‘adoption’ by farmers. There are many experiences where adoption claimed during the course of active promotion of technologies by NGOs and research later transpired to be due to the temporary influence of the project, rather than a sustained change in agricultural practice. For example, the apparent success of Sasakawa Global 2000 in promoting CA (Ito et al., 2007) appears largely to have been due to its promotion within a technology
Conclusions: defining a socio-ecological niche for CA in sub-Saharan Africa
Knowler and Bradshaw (2007) concluded on the basis of a world-wide study that there was a lack of universal variables that explain the adoption of conservation agriculture and that efforts to promote conservation agriculture need to be tailored to local conditions. This resonates with the conclusions of Erenstein (2002) and Kronen (1994) that the potential of CA and soil conservation technologies in general, is site-specific and depends on the local bio-physical and socio-economic environments.
Acknowledgements
We thank six anonymous referees for their careful reading, critical reviews and useful suggestions on an earlier manuscript.
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