Nepal’s Kanchenjunga Conservation Area (KCA) is one of the most unique experiments in community-managed nature protection in the Himalaya.
The landscape below the world’s third highest mountain in eastern Nepal supports globally significant biodiversity, including the endangered snow leopard, red panda, musk deer, and black bear.
But it also sustains mountain livelihoods, pastoral systems, tourism economies, and transboundary cultural connections. Yet, the region is experiencing expansion of hydropower and roads, tourism growth that put pressure on an ecologically fragile high mountain system.
This is occurring at a time when Himalayan ecosystems are already under mounting pressure from climate breakdown, shifting precipitation patterns, glacier instability, biodiversity loss, and rapid socioeconomic change.
The KCA is no longer just a protected landscape: it has become a contested socio-ecological space where development aspirations, conservation priorities, local livelihoods, and institutional responsibilities increasingly intersect and at times, conflict.
Residents and tourism entrepreneurs recognise the need for conservation management, but also want the KCA Management Council (KCAMC) to be more active in maintaining trekking trails, bridges, rest shelters, and other tourist facilities damaged by landslides or weather extremes.
Residents want greater transparency regarding taxes, royalties, and conservation-related fees. Economic status varies considerably across the region, and not all families have equal landholdings, tourism income, or market access. Taxes and fees are a disproportionate burden on families.
Yak herders are among the most vulnerable livelihood groups and describe the growing challenges of maintaining traditional pastoral systems under changing ecological and socioeconomic conditions. Coexistence with wildlife has always been a part of their culture and identity, but they suffer increasing livestock depredation by snow leopards and wolves.
Herders are not happy with insurance compensation rates, verification procedures, delayed response, and the valuation of losses. They have limited representation in conservation committees, decision-making bodies, and local governments. Herders do not want to be merely viewed as beneficiaries or victims, but rather as essential conservation partners whose ecological knowledge and lived experiences are critical for long-term coexistence.
The suspension of cross-border livestock trade with China after the pandemic has created additional economic stress, reducing household income and altering herd management systems. Many households have larger livestock populations than before, increasing grazing pressure on high and intensifying competition between domestic animals and wild herbivores such as blue sheep an important prey species for snow leopards.
This changing pastoral dynamic may also be increasing carnivore attacks on livestock. Human–wildlife conflict within KCA is not just a conservation issue, but is connected to transboundary trade, rural economies, grazing governance, and disruptions in people-to-people relations.
Residents want better veterinary services, livestock vaccination programs, and technical support to meet international livestock health standards required for cross-border trade. Many participants argued that improved diplomatic coordination and institutional trust-building between Nepalese and Chinese authorities could help restore sustainable livestock markets while reducing ecological and economic pressure within mountain grazing systems.
UPWARD MOVEMENT
The upward movement of development is one of the most visible and complex transformations in the landscape. Roads carved into steep slopes, hydropower plants, transmission lines, and construction camps are in remote areas previously accessible only by foot trails.
The changes are visible all along the road from Phungling toward Olangchung Gola and from Sekathum to Ghunsa. For someone born and raised in this region, I felt a profound emotional contradiction.
On the one hand, remote mountain communities need connectivity, healthcare, electricity, communication systems, and economic opportunities. Villagers who once walked for days to access basic services deserve the same developmental opportunities available elsewhere.
Yet as a researcher and student of Himalayan ecology, it was equally heartbreaking to witness the scale of environmental disturbance. Scarred mountainsides, sediment-filled rivers, and rivers obstructed by hydropower plants raise difficult questions about the long-term ecological consequences of such development.
Can development and conservation truly coexist within fragile mountain ecosystems, or will one inevitably dominate the other? Rivers, forests, wildlife, glaciers, and mountains are also living systems. How would they respond if they possessed the ability to resist human transformation? What would ecological revolt look when nature defends itself?
Then, I remembered the realities of growing up in a remote Himalayan village: the long walks, isolation, kerosene lamps and limited healthcare and communication. Development is not inherently destructive: the challenge lies in determining what form of development is appropriate, sustainable in ecologically sensitive mountains.
Nepal’s renewable energy expansion and carbon neutrality targets complicates this debate even more. Hydropower is promoted as a clean and climate-friendly energy that can boost economic growth and reduce dependence on fossil fuels.
In the KCA, the cumulative ecological impact of multiple hydropower projects within connected river systems remain poorly understood.
A divergence of views and lack of coherence can be seen in the management committees between local communities, local governments, and local governments. The ultimate shared objective is still the effective conservation and sustainable management of the landscape and its natural resources.
The existing tensions therefore should not be interpreted solely as institutional failure, but rather as the outcome of multiple actors with different responsibilities, mandates, expectations, and operational limitations within an increasingly complex socio ecological landscape.
The decisions of government officials are frequently shaped by legal frameworks, national policies, bureaucratic procedures, budgetary limitations, and institutional hierarchies. In contrast, the conservation council sees local realities, community management practices, practical field-level challenges, and the day-to-day concerns of residents.
Both perspectives may be valid but differences in interpretation, implementation priorities, and jurisdictional authority can create gaps in communication, coordination, and trust. Being a government official myself, I understand that many decisions are constrained by laws, institutional procedures, national priorities, and administrative systems.
The local conservation council on the other hand must directly respond to diverse community expectations, local grievances, livelihood concerns, and rapidly changing socioeconomic realities. Balancing these multiple pressures is not easy for either side, particularly in remote Himalayan regions where conservation, development, and political expectations intersect simultaneously.
The two expectations can collide and create conflict. Similar tensions can emerge between local governments and the KCAMC regarding resource allocation, development priorities, implementation authority, and spatial jurisdiction. Broader social diversity, differing ideological perspectives, and varying stakeholder interests can also shape decision-making processes and affect conservation.
Increasing financial inflow of hydropower development projects, particularly through corporate social responsibility programs and community support funds, have introduced additional dynamics among local stakeholders.
Despite advantages, there is also growing concern regarding transparency, accountability, and the equitable distribution of such benefits. Council members want ecologically responsible financial mechanisms that ensure a portion of development-related revenue is allocated toward long-term biodiversity conservation, ecological restoration, disaster risk reduction, and environmental monitoring.
Nature conservation should not be viewed as separate from development, but rather as the ecological foundation upon which long-term development ultimately depends. Freshwater availability, sustainable tourism, slope stability, climate resilience, hydropower generation, agricultural productivity, and ecosystem services all rely upon functioning natural systems.
Development activities within and around conservation areas require careful planning, cumulative impact assessment, and long-term ecological safeguards to ensure sustainability for both people and nature.
Land use and land cover within the KCA were assessed using season-wise land cover datasets. Ecological conditions were further evaluated using satellite remote sensing images.
The analysis revealed substantial environmental transformation between 2005 and 2020. Although bare rock, glaciers, grasslands, and forests continued to dominate the landscape, significant shifts occurred within these ecosystems.
Forest cover declined from 372.41 km² (18.7%) to 324.89 km² (16.3%), while bare rock decreased from 467.75 km² to 395.32 km². In contrast, grasslands expanded from 425.59 km² (21.4%) to 484.15 km² (24.3%), and snow-covered areas increased from 181.06 km² to 230.27 km². Glacier extent remained relatively stable, declining only slightly from 434.77 km² to 433.61 km².
Human-modified land uses also expanded, with built-up areas increasing nearly fivefold and cropland showing gradual growth. These changes suggest the combined influence of climatic variability, ecological succession, tourism growth, infrastructure expansion, and changing livelihood practices.
Ecological indicators revealed widespread vegetation greening across lower and middle elevation zones, but this was not accompanied by higher ecosystem productivity. The data showed that increasing vegetation cover does not necessarily correspond to improved ecosystem functioning.
Land Surface Temperature remained relatively stable, with maximum values ranging from 20.4°C in 2005 to 19.7°C in 2020, whereas precipitation exhibited substantial variability, ranging from 1101–1877 mm in 2005, 1450–2276 mm in 2010, and 946–1965 mm in 2020.
Despite growing socioeconomic pressures, institutional complexities, and ecological uncertainties, community-based conservation within the KCA has generated important social and environmental gains. Local communities, conservation council members, and local residents described improvements in anti-poaching activities, wildfire control, conservation awareness, tourism opportunities, livelihood diversification, and public participation in environmental stewardship.
Yet conservation governance remains complex because local governments, conservation institutions, hydropower developers, tourism operators, and local residents often operate under different priorities, mandates, and expectations.
Effective conservation in the eastern Himalaya therefore requires moving beyond fragmented governance toward collaborative, transparent, and science-based approaches grounded in trust, participation, and ecological responsibility. Strengthening dialogue, improving benefit-sharing mechanisms, economic valuing of nature, integrating Indigenous and local ecological knowledge, supporting cumulative environmental assessments, and investing in long-term ecological monitoring systems are all essential for sustaining coexistence between people and nature.
At the same time, the region continues to face major scientific data gaps. Despite growing evidence of ecological and climatic change, the conservation area still lacks sufficient long-term ecosystem, hydrological, and biodiversity monitoring infrastructure across elevation gradients.
The Snow Leopard Research Centre at Khambachen represents an important step toward strengthening high-altitude ecological research in the KCA n the Kanchenjunga Conservation Area, but it needs further support.
In addition, there is a critical need to strengthen data management systems, long-term data storage, and the localisation of data-driven decision-making processes. Enhancing the technical capacity of KCA officials and conservation practitioners through targeted training and institutional support will be equally crucial for improving evidence-based conservation planning, ecological monitoring, and adaptive management.
Ultimately, the future of KCA will depend upon whether development and conservation can evolve through mutual adaptation rather than working at cross purposes. The eastern Himalaya is not merely a frontier for infrastructure expansion, but one of the world’s most ecologically and culturally significant mountain landscapes.
Its glaciers regulate water systems, forests stabilise fragile slopes, rivers sustain downstream populations, and landscapes support biodiversity, tourism, and cultural identity across scales far beyond the conservation area itself. Protecting this gift of nature requires collective responsibility shared among governments, conservation councils, scientists, local communities, and development actors alike.
It will require balancing aspiration with restraint, economic opportunity with ecological safeguards, and short-term development interests with long-term environmental sustainability for future generations.
Chungla Sherpa is a PhD researcher at Lincoln University, New Zealand, working in conservation ecology and mountain biodiversity focusing on predator–prey interactions, and community-based conservation in the Himalaya.