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Growing the Wealth of the Poor - World Resources Institute

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170for many nature-based enterprises. The state has a clear role indefining, encouraging, and enforcing sustainable naturalresource management. Based on its synoptic view <strong>of</strong> <strong>the</strong>nation’s ecosystems, <strong>the</strong> state must make sure that local resourceexploitation patterns are compatible with <strong>the</strong> national vision forresource management and, when summed toge<strong>the</strong>r, do notdegrade <strong>the</strong> resource base. However, governments have atendency toward heavy-handed regulation <strong>of</strong> communitygroups who manage natural resources. This <strong>of</strong>ten manifests asstrict prescriptions for “best practices” that communities arerequired to follow or complex management plans that <strong>the</strong>y mustformulate before being granted <strong>the</strong> necessary permits to harvestor carry out management activities. In many cases <strong>the</strong>seprescriptions are unnecessarily complex, do not respect localinstitutions or capacities, and impose a severe financial burden(Ribot 2004:54–59; Molnar et al. 2007:64–70). Thus, regulationsthat may be appropriate for industrial-scale enterprisesmanaging large tracts <strong>of</strong> forest or significant fishing fleets can beoverkill for small community-based enterprises, resulting in acompetitive disadvantage.Under Cameroon’s 1994 Forestry Law, for example, <strong>the</strong>requirements for establishing a community forest include creatinga management committee with a constitution, mapping <strong>the</strong>forest areas at issue and comparing <strong>the</strong>m to <strong>the</strong> government’soverall forest plan, and submitting a forest management plan.These steps have proved too complex and expensive for mostcommunities (Ribot 2004:55). Similar planning and permitobstacles plague forest users in many o<strong>the</strong>r countries, includingIndia, Nepal, Tanzania, Bolivia, Guatemala, Senegal, and <strong>the</strong>Philippines. In Guatemala’s community forest concessions in <strong>the</strong>Petén region, <strong>the</strong> overlapping inspection requirements <strong>of</strong> donors,international certifiers (<strong>the</strong> Forest Stewardship Council), andgovernment agencies burdened fledgling enterprises with highcosts and hindered <strong>the</strong>ir transition to financial independence. In2007, a survey <strong>of</strong> community forestry enterprises worldwidefound that artificial and overdemanding rules for managementplans and o<strong>the</strong>r required permits and procedures—and <strong>the</strong> highcosts associated with <strong>the</strong>m—were major obstacles to <strong>the</strong> success<strong>of</strong> community-based businesses (Molnar et al. 2007:66–70).Overzealous government oversight and micromanagement<strong>of</strong> community enterprises amounts to resistance to true devolution<strong>of</strong> resource rights to local communities. It <strong>of</strong>ten stems fromfear by government bureaucrats that rural communities lack <strong>the</strong>capacity—and <strong>the</strong>refore cannot be trusted—to manage resourcesresponsibly and efficiently. This lack <strong>of</strong> “capacity” is used as anexcuse to delay granting <strong>the</strong> necessary government permission,<strong>of</strong>ten without <strong>of</strong>fering any avenue or resources for gaining <strong>the</strong>required capacities or meeting <strong>the</strong> required standards. The netresult is that <strong>the</strong> government retains its accustomed role at <strong>the</strong>center <strong>of</strong> resource management (Ribot 2004:59–65).An alternative to <strong>the</strong> over-regulation <strong>of</strong> community-basednatural resource enterprises would be to adopt a “minimumstandards” approach. The national government would establisha minimum set <strong>of</strong> rules or standards that communitymembers must follow in <strong>the</strong>ir management but would grantcommunities flexibility in how <strong>the</strong>y meet this standard. Forinstance, environmental standards could be set for how much<strong>of</strong> a forest can be cut in a single year, what rare or endangeredspecies are not to be harvested, or what seasons are <strong>of</strong>f-limitsfor fishing in order to encourage spawning and stock replenishment.On <strong>the</strong> o<strong>the</strong>r hand, all activities not specified in <strong>the</strong>environmental rules or not at odds with <strong>the</strong> environmentalstandard would be allowed without <strong>the</strong> need for a permit ormanagement plan. This would reverse <strong>the</strong> current regulatorystructure in which only activities specified in <strong>the</strong> managementplan are allowed (Ribot 2004:56–59).Minimum environmental standards or targets couldprovide <strong>the</strong> flexibility that local groups need to adapt andinnovate in <strong>the</strong>ir management without compromising sustainability.Of course, this would only be possible if reasonablesanctions were in place for breaching <strong>the</strong> standards, such asfines or temporary loss <strong>of</strong> harvest rights. As in any regulatoryscheme, credible monitoring and enforcement would be crucial.Simplicity and clarity <strong>of</strong> <strong>the</strong> standards and <strong>the</strong> consequences <strong>of</strong>failure to meet <strong>the</strong>m would also be a key factor in <strong>the</strong> success <strong>of</strong>this approach (Ribot 2004:56–59).In addition to <strong>the</strong>ir substantial regulatory burden, smallnature-based enterprises also commonly suffer from inappro-

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