Rachel Wynberg 61
One of the main effects of CITES has been a decline in market demand,
but it has also given renewed impetus to domestication and cultivation efforts,
stemming from the perceptions created of an endangered resource. Although
Appendix II allows for ‘controlled trade’ in a species rather than imposing an
outright ban, successful listing will undoubtedly affect trade from the wild—and
thus the livelihoods of thousands of harvesters dependent on the resource for
income. Including Harpagophytum on Appendix II, it is argued, will shift the
market towards preferring a cultivated product over one that is wild harvested,
and thus an environment that favours agribusiness and commercial farmers
over and above marginalised small farmers and local livelihoods (CRIAA SA-DC
2000a). A major concern in this regard is the role played by South Africa in
successfully cultivating Harpagophytum and its potential, as a highly developed
agricultural economy, to completely usurp production of devil’s claw in the
region and make wild harvesting redundant (Cole and du Plessis 2001). Planned
cultivation projects outside of range states present a similar threat for harvesting
communities and national economies in southern Africa.
What are the inputs required for cultivation and how might these restrict
the involvement of small farmers and marginalized people in these activities?
Although specific information is difficult to come by, irrigation is an essential
requirement for devil’s claw cultivation, estimated by some to be 6 liters of
water per plant per week (Powell and Moolman 1999). Such requirements are
clearly an impediment for marginalized communities in remote settlements,
few of which have access to potable water let alone sufficient quantities for
irrigation. Also pertinent is the question of the willingness and ability of
communities to engage in devil’s claw cultivation and the importance of (often
nonexistent) extension services to support such activities (Matlhare 1994). The
reality of the situation, borne out by the majority of experiences and by the
stated interest of commercial farmers, is that cultivation of devil’s claw is most
likely to be pursued by economically privileged farmers with ready access to
water, land, transport and knowledge.
This notwithstanding, many of those engaged in the devil’s claw trade in
southern Africa see cultivation as an inevitability that should be controlled and
turned to their best advantage, rather than an activity that should be prohibited
on the basis of its social impacts. The issue is obviously not cut and dry, nor the
potential impacts. Although often touted as a solution to unsustainable use,
Harpagophytum cultivation brings with it its own set of environmental problems,
notably those associated with soil erosion, land clearing, increased salinity and
genetic uniformity. Strict controls on cultivation, such as those introduced
recently by the Namibian government, clearly require widespread monitoring,
adherence and application throughout the region.
SOCIAL AND CULTURAL ASPECTS OF DEVIL’S CLAW PRODUCTION
Devil’s claw production in southern Africa takes place in some of the most
inhospitable and arid parts of the region, considered marginal for conventional
agricultural production and suitable mostly for grazing. Livelihood options are
thus extremely limited, and devil’s claw extraction is a highly important survival
strategy for the poor. Indeed, the 9,000 or so devil’s claw harvesters represent
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