Northern Rangelands Trust
Northern Rangelands Trust (NRT) is a conservation network founded in 2004 by Ian Craig and Delia Craig that coordinates community-based wildlife conservancies across northern Kenya's arid and semi-arid rangelands. Representing a significant paradigm shift in African conservation, the NRT model integrates pastoral communities as conservation partners through formal community conservancies, providing employment, tourism revenue, and governance participation while managing approximately 44,000 square kilometers through 43 member conservancies.
The NRT's founding reflected a deliberate rejection of fortress conservation models that had excluded pastoral communities. Ian Craig and Delia Craig recognized that pastoral communities had sustainably managed rangelands for millennia and that conservation exclusion of these communities was both unjust and unsustainable. The trust was established to provide technical assistance, funding, training, and market linkages enabling pastoral communities to manage their own lands for wildlife conservation while deriving economic benefits through tourism, ranger employment, and conservation-related infrastructure.
The network's geographic scope is extraordinary. Spanning from the Laikipia Plateau through Samburu, Isiolo, and Marsabit counties, the NRT's member conservancies encompass some of East Africa's most important wildlife habitat and pastoral rangelands. The network protects endangered species including Grevy's zebra, African wild dogs, and reticulated giraffes while providing livelihood diversification for pastoral communities historically dependent on livestock production vulnerable to drought and market volatility.
The NRT model creates explicit economic incentives for conservation by channeling tourism revenue to communities that manage conservancies. Conservancies charge visitor fees and offer lodge concessions that generate income available for ranger salaries, development projects, and community benefits. This revenue-sharing mechanism theoretically aligns conservation with community economic interests, creating incentive for wildlife protection. The model recognized that conservation requires sustained community cooperation and that cooperation depends on demonstrable economic return.
Community ranger employment represents a major employment program across northern Kenya. The NRT coordinates thousands of community rangers who conduct wildlife protection, anti-poaching patrols, habitat monitoring, and wildlife conflict management. Ranger employment provides training, livelihood, and economic opportunity in regions with limited employment alternatives. The ranger program has created a cadre of Kenyan conservation workers while building conservation capacity within communities rather than importing external expertise.
Wildlife corridor protection through NRT conservancies maintains habitat connectivity across the landscape. The critical Laikipia-Samburu corridor, connecting central and northern Kenya's wildlife populations, is protected through coordinated conservancy management. Corridor protection enables wildlife movement between fragmented habitats, maintaining genetic connectivity and population resilience. The landscape-scale approach recognizes that wildlife conservation requires habitat networks rather than isolated protected areas.
Climate adaptation through conservation diversification has become increasingly central to NRT operations. Northern Kenya's pastoral communities face increasing drought and climate variability that threatens livestock-dependent livelihoods. The NRT explicitly frames conservation as climate adaptation strategy, providing livelihood diversification that enhances community resilience to climate-driven shocks. Conservancy revenues during drought periods support communities when pastoral production collapses, preventing catastrophic livelihood loss.
However, the NRT model faces significant challenges and critiques that expose tensions between conservation and pastoral interests. The 2017 Laikipia invasions demonstrated underlying community frustrations with conservancy models, with pastoral communities protesting land access restrictions and arguing that benefits remained concentrated in conservation establishment hands. Invasions specifically targeted conservancies, suggesting that community participation had not achieved consensus on conservation priorities or benefit distribution equity.
Some critics argue that conservancies restrict pastoral livelihoods and grazing access disproportionately, despite formal community participation in management. Wildlife protection on conservancy lands reduces available grazing area at precisely the time when pastoral communities face increasing pressure from population growth and climate variability. The benefit distribution from tourism revenue, while real, may not fully compensate for grazing access restrictions, particularly for poorer pastoral households excluded from ranger employment and lodge operations.
Tourist demand and market risks pose significant sustainability challenges. Conservancy revenue depends on international and domestic tourist demand, vulnerable to global economic fluctuations, security concerns, and pandemic disruptions. The COVID-19 pandemic devastated conservancy revenues in 2020, creating financial crisis for communities dependent on tourism income. Diversifying conservancy economies beyond tourism remains essential but underdeveloped in many member conservancies.
Land tenure security, improved through the Community Land Act (2016), provides greater confidence in conservancy sustainability, yet questions persist about whether formal community conservancies can persist without consistent external funding and technical support. The NRT's effectiveness depends substantially on continued organizational capacity and resource availability from the trust itself, creating sustainability questions about long-term viability if external funding declines.
See Also
- Ian Craig - Co-founder and visionary leader
- Delia Craig - Co-founder and strategic architect
- Community Conservancies Model - Broader conservancy framework
- Wildlife Corridors Kenya - Habitat connectivity and landscape integration
- Pastoralists and Conservation - Community participation and land use tensions
- Laikipia Plateau - Northern boundary and original conservancy base
- 2017 Laikipia Invasions - Community contestation of conservancy model
- Climate Change and Wildlife - Climate adaptation through conservation
Sources
- Northern Rangelands Trust official publications and strategic documents
- NRT annual reports and impact assessments
- Lamprey, R.H. & Reid, R.S. (2004). Expansion of Human Settlement in Kenya's Maasai Mara: What Conservation Policy Implications? Biological Conservation, 123(2), 267-277.
- Oldekop, J.A. et al. (2016). A Comparative Assessment of Social and Environmental Impacts from Private and Community-Based Ecosystem Conservation Approaches. Global Environmental Change, 40, 89-101.
- Karenyi, N. (2008). Community-Based Conservancies in Kenya: A Preliminary Assessment of Social and Economic Impacts. Conservation and Development, 15(3), 18-29.