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Managing the Miombo Woodlands of Southern Africa - PROFOR

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<strong>the</strong> region, and grassy patches within <strong>the</strong> woodlands are sometimes heavily used for grazing. The<br />

miombo woodland comes into its own during <strong>the</strong> late dry season, when new leafy foliage is <strong>of</strong>ten<br />

<strong>the</strong> only available source <strong>of</strong> browse for livestock. The relationship between woodland use, livestock<br />

management, and crop production is highly synergistic: livestock depend on miombo resources for<br />

grazing and browse; <strong>the</strong>y process and transfer nutrients, from woodlands, via manure, to cropped<br />

fi elds; and soils are <strong>of</strong>ten supplemented by composted leaf litter collected from woodlands. <strong>Miombo</strong><br />

is also heavily used for beekeeping. Somewhere around 100 million people live in <strong>the</strong> miombo<br />

region, and to some extent, depend on it for income and consumption goods.<br />

Household studies have documented <strong>the</strong> importance <strong>of</strong> miombo to rural households. The studies<br />

show that poor rural households are vitally dependent on miombo woodlands because <strong>of</strong> <strong>the</strong>ir<br />

role as a safety net, not that poor rural households are becoming rich by tapping into markets<br />

for miombo products (or have much potential for doing so). Among <strong>the</strong>se households, miombo<br />

is providing for a very substantial proportion <strong>of</strong> total household consumption. This proportion<br />

increases signifi cantly in households that encounter serious income shocks because <strong>of</strong> illness or<br />

environmental stress. The household studies show that miombo woodland resources are a critical<br />

element <strong>of</strong> <strong>the</strong> rural household economy and contribute signifi cantly to mitigating <strong>the</strong> impacts <strong>of</strong><br />

poverty. If <strong>the</strong>se resources are lost as a result <strong>of</strong> deforestation or o<strong>the</strong>r proximate causes, <strong>the</strong> need<br />

for alternative safety nets is likely to place fur<strong>the</strong>r large burdens on public service delivery institutions,<br />

already poorly equipped to handle <strong>the</strong> problem <strong>of</strong> rural poverty. Spatial analysis (for example, in<br />

Malawi and Mozambique) confi rms <strong>the</strong> statistical correlation between areas with extensive miombo<br />

cover and areas with high poverty rates.<br />

In light <strong>of</strong> <strong>the</strong> role miombo plays in poverty mitigation, we examine <strong>the</strong> question <strong>of</strong> why <strong>the</strong>se<br />

woodlands are not better managed. The fact that miombo produces relatively few high-value<br />

timber products means that it has not supported <strong>the</strong> development <strong>of</strong> much <strong>of</strong> a forest industry (or<br />

related public institutions). The forest institutions that are in place have become largely irrelevant<br />

for management, as commercially viable timber stocks have been logged over and management <strong>of</strong><br />

high-value species has been problematic. At least for <strong>the</strong> rural poor, miombo needs to be managed<br />

for multiple outputs. This is not easy, both because <strong>the</strong> silviculture <strong>of</strong> managing for multiple outputs<br />

is poorly understood and because <strong>the</strong> complexity <strong>of</strong> <strong>the</strong> management system is vastly increased<br />

when multiple stakeholders have interests in managing for different outcomes.<br />

Forest policies, institutions, and legislation are <strong>of</strong>ten disenabling, and are seldom aligned with<br />

management objectives that favor <strong>the</strong> rural poor. Mostly, this has meant that rights to use and<br />

access miombo resources have been retained by <strong>the</strong> state (even in <strong>the</strong> face <strong>of</strong> trends toward<br />

decentralization). The policy framework may prohibit <strong>the</strong> harvesting <strong>of</strong> woodland products for<br />

commercial purposes, except under limited circumstances. Even when <strong>the</strong>re is potential for working<br />

with local producers to improve management by, for example, improving <strong>the</strong>ir extractive techniques<br />

or conversion effi ciencies (e.g., from roundwood to charcoal), <strong>the</strong> legal framework may not allow<br />

it. A burdensome regulatory framework has meant that it is easy to be illegal. The regulatory<br />

framework <strong>of</strong>ten does little more than improve <strong>the</strong> ability <strong>of</strong> petty <strong>of</strong>fi cials to extract informal<br />

payments. Devolution <strong>of</strong> control over natural resources to local forest users, while <strong>of</strong>fering good<br />

potential, has seldom been undertaken wholeheartedly. It is this lack <strong>of</strong> effort that has undermined<br />

what are ostensibly promising policies for improving woodland management.<br />

6 MANAGING THE MIOMBO WOODLANDS OF SOUTHERN AFRICA

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