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American Bison - Buffalo Field Campaign

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The problems of governance and scale have been well<br />

discussed in the literature (Westley and Miller 2003; Wilke et<br />

al. 2008). There typically is a wide range of actors associated<br />

with the conservation of large landscapes and species with<br />

large spatial needs such as bison. It is easy to underestimate<br />

the complexity of ownership patterns on large landscapes<br />

and to miss identifying key actors on this conservation stage.<br />

Furthermore, different kinds of actors will have different rights,<br />

interests, and capacities, and will need to be approached in<br />

different ways (Wilke et al. 2008). The challenge of forming<br />

complex partnerships at the appropriate scale is formidable and<br />

often discourages efforts to consider large-scale initiatives.<br />

8.4.1.1.4 Defining the social and economic value<br />

of wild bison<br />

Many legal and policy changes necessary for the ecological<br />

restoration of bison are linked to social and economic factors.<br />

Agencies and conservationists need to identify the economic,<br />

social, and ecological benefits of restoring wild free-ranging<br />

bison, while protecting existing cultural and economic interests<br />

(Geist 2006). The value of restoring wild bison must be<br />

expressed in a manner that does not necessarily diminish the<br />

economic value of existing livestock and commercial bison<br />

markets managed under an agricultural paradigm. This may take<br />

creative approaches involving policy adjustments and paradigm<br />

shifts among cooperating agencies/private sectors that optimise<br />

complimentary land use strategies and mitigate identified<br />

conflicts. This process could be supported by tax incentives,<br />

payment for environmental services, ecotourism, incentives for<br />

landowner cooperation (e.g., Colorado’s Ranching for Wildlife<br />

Program), extension services, and training for a new generation<br />

of landowners and managers.<br />

8.4.1.1.5 Coordination of policies, rules, and<br />

regulations by government<br />

Coordination of management policies, rules, and regulations<br />

(or the lack thereof) by various governments has also hindered<br />

bison conservation efforts. Because no single government<br />

agency owns or manages sufficiently large blocks of land to<br />

sustain free-ranging bison, cooperation between agencies<br />

is needed for restoration and conservation planning and<br />

implementation. Many agencies’ missions are not readily<br />

compatible with cooperative management strategies needed<br />

for conservation of bison at large scales. Furthermore, many<br />

land management agencies have directed missions and goals<br />

that may not immediately support the types of policy changes<br />

required to manage for the conservation of bison. In addition<br />

to coordination among government agencies there is often a<br />

compelling need to coordinate with and among Tribal and private<br />

lands influenced by other policies and management objectives.<br />

76 <strong>American</strong> <strong>Bison</strong>: Status Survey and Conservation Guidelines 2010<br />

8.4.1.1.6 Agricultural conflicts among<br />

mixed land ownership<br />

The most significant conflicts associated with restoring wild free-<br />

ranging bison are likely to be with agricultural neighbours living<br />

near conservation reserves. Establishing free-ranging wild bison<br />

herds in North America will undoubtedly lead to conflicts from<br />

crop damage, forage competition with livestock, mixing with<br />

livestock, possible interbreeding with cattle, disease issues, and<br />

damaging private property. These agricultural conflicts are not<br />

entirely uncommon with other large herbivores.<br />

These six policy obstacles are quite common across<br />

international, state/provincial, and public/private jurisdictional<br />

boundaries within the original range of bison. <strong>Bison</strong> restoration<br />

must occur at sufficiently large landscape scales that few, if<br />

any, individual agencies will be able to implement an effective<br />

management programme on their own. Coordination of agency<br />

missions to conserve wild bison must in the long run be a<br />

negotiated process to ensure joint conservation goals can be<br />

established and implemented within the legal framework. In<br />

addition, conservation goals must be established to encourage<br />

privately owned populations of wild bison (as defined elsewhere<br />

in this document) to be managed over the course of many years<br />

in a manner that allows ranchers to build new markets that<br />

provide economic benefits for conserving the characteristics of<br />

ancestral bison herds.<br />

Other obstacles to restoration include: long time scales,<br />

institutional resistance, funding, and conservation mission<br />

creep. Most large-scale conservation projects for long-lived<br />

mammals need to play out across long time scales. It is easy<br />

for conservation partners to fatigue, and for shifting political<br />

and social climates to make extended time scales problematic.<br />

Institutional resistance is inevitable within and among the<br />

cooperating agencies and private sector partners involved in<br />

a bison restoration project. Within agencies and organisations<br />

there is likely to be some internal resistance to various aspects<br />

of the project, so care will be needed to build reasonable<br />

consensus. Although many agency or private groups may<br />

support the concept of restoration, there is a fundamental need<br />

for funding and contribution from all critical partners. Finally, with<br />

every conservation programme, the implementation can creep<br />

off target or move beyond intended goals. This has a tendency<br />

to dismantle social and political support for a project by creating<br />

a different type of management or objective than was originally<br />

identified and agreed upon by stakeholders. For example as<br />

landscapes become larger, and some measure of success is<br />

achieved, there may be a tendency to move the conservation<br />

focus. Conservation and restoration strategies and planning<br />

efforts need to clearly articulate the conservation goal and be<br />

able to measure progress and identify critical benchmarks for<br />

meeting those goals.

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