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Rajasthan Has 149 Tigers, But Can They Move Safely?

9 min read

Aug 01, 2026

Tiger Conservation
Tiger Corridors
Biodiversity
Environment and Ecology
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A Conservation Milestone Worth Celebrating

Rajasthan’s tiger population reached 149 as of July 28, 2026, rising from 135 in 2025. These tigers are distributed across the state’s five tiger reserves, with Ranthambore continuing to support the largest share of the population.

The increase deserves recognition. Rajasthan contains vast dry landscapes, expanding settlements, mining zones, highways, railway lines, and areas with intense tourism activity. Protecting a growing population of large carnivores in such a setting requires sustained monitoring, habitat management, prey conservation, community participation, and protection against poaching.

The rise also reflects India’s broader success under Project Tiger. The country has moved from a period when local tiger populations were disappearing to becoming home to the largest wild tiger population in the world.

However, population numbers alone cannot tell us whether tiger conservation is secure.

A reserve may report more tigers while the surrounding landscape becomes increasingly fragmented. Roads, railway lines, mines, settlements, resorts, transmission corridors, and other projects can gradually isolate one tiger population from another.

This creates the central challenge facing Indian tiger conservation today.

India has become better at protecting tigers inside reserves. It has not shown the same consistency in protecting the corridors that connect those reserves.

Why Tiger Corridors Matter

A tiger corridor is a stretch of forest, scrubland, riverine habitat, farmland, or mixed landscape that allows tigers to move between larger habitat areas.

These corridors are not always dense and untouched forests. Some pass through villages, agricultural land, revenue forests, mining zones, and areas crossed by roads or railway tracks.

Their ecological value lies in connectivity.

Young tigers, particularly males, often leave the territories where they were born and search for new areas. This movement reduces competition, allows new territories to be established, and enables genetic exchange between populations.

When two reserves remain connected, a tiger from one population can breed with a tiger from another. This movement introduces new genetic material and reduces the risk of inbreeding.

When corridors are blocked, tiger reserves begin to function like ecological islands.

The tigers may remain physically protected inside those islands for several years. Their numbers may even rise temporarily. But isolation gradually weakens the long term stability of the population.

The Danger of Ecological Islands

A protected reserve surrounded by highways, towns, mines, farms, and industrial projects may appear successful because it still contains tigers.

Yet such a reserve can become an ecological trap.

As the tiger population grows within a limited area, territorial competition increases. Younger animals are forced towards the boundary. If safe dispersal routes do not exist, they may enter villages, cross dangerous roads, attack livestock, or come into conflict with people.

Some may be killed in vehicle collisions. Others may die in territorial fights. A few may be captured and relocated after being labelled as problem animals.

The deeper issue is not simply that tigers are leaving the reserve. Dispersal is a natural biological process.

The problem is that the surrounding landscape no longer allows dispersal to happen safely.

An isolated reserve also faces genetic risks. When animals repeatedly breed within a small population, genetic diversity declines. Harmful traits can become more common, fertility may fall, disease vulnerability may rise, and the population may become less adaptable to environmental change.

These effects are not always visible immediately. A reserve can report increasing tiger numbers while genetic resilience is silently weakening.

This is why a successful tiger census does not automatically indicate a secure tiger population.

Rajasthan’s Connectivity Challenge

Rajasthan’s tiger reserves do not exist as one continuous habitat.

Ranthambore, Sariska, Mukundra Hills, Ramgarh Vishdhari, and Dholpur Karauli are located within landscapes shaped by human activity. Their future depends on whether functional connections can be maintained between forests in Rajasthan and neighbouring tiger landscapes.

The Ranthambore landscape is especially important because it acts as a major source population. Tigers born there have dispersed towards other forest areas, contributing to the recovery or establishment of populations beyond the reserve.

However, this movement brings animals into contact with roads, farms, villages, tourism infrastructure, and development projects.

The Aravalli landscape around Sariska faces a different but equally serious challenge. Mining, real estate pressure, roads, settlements, and land use change have fragmented important wildlife habitats.

Mukundra Hills and Ramgarh Vishdhari require suitable prey populations and secure movement routes if they are to support viable breeding populations rather than depend continuously on relocation from other reserves.

Dholpur Karauli also has strategic value because of its relationship with adjoining forest landscapes and potential movement routes.

The central conservation question is therefore not simply how many tigers each reserve contains.

It is whether tigers can move between these landscapes without encountering deadly barriers.

Highways and Railway Lines as Biological Barriers

Transport infrastructure is one of the most visible threats to wildlife connectivity.

A highway passing through a tiger corridor may appear narrow on a map, but its ecological impact can extend far beyond the width of the road.

Fast traffic creates noise, light, pollution, and collision risks. Dividers, fencing, service roads, roadside construction, and commercial development can make the barrier even stronger.

Railway lines create similar dangers. Tigers and their prey may be struck by trains, particularly where tracks pass through forests or movement routes.

Infrastructure can also create secondary fragmentation. Once a road is built, settlements, shops, resorts, warehouses, and other projects often emerge around it. A corridor that was initially narrowed may eventually be lost completely.

Wildlife underpasses, overpasses, speed controls, fencing, and route modification can reduce these impacts. However, such measures work only when they are based on reliable ecological data and incorporated during project planning.

Adding a poorly located underpass after construction cannot fully restore a corridor that has already been fragmented.

Mining and the Slow Loss of Connectivity

Mining creates another major threat, particularly in landscapes containing minerals, stone, and other commercially valuable resources.

A mining lease does not affect only the exact area where extraction occurs. It can also require access roads, worker settlements, crushing units, waste disposal areas, power lines, and regular heavy vehicle movement.

Blasting, noise, dust, groundwater extraction, and vegetation removal can make a wider landscape unsuitable for wildlife movement.

The cumulative effect is especially important.

One small project may appear manageable when evaluated independently. Several mines, roads, railway expansions, resorts, and settlements within the same corridor can collectively destroy its ecological function.

Environmental appraisal often examines individual projects. Tigers, however, experience the combined landscape.

India therefore needs corridor level impact assessments rather than approvals based only on isolated project boundaries.

The NTCA and Landscape Level Conservation

The National Tiger Conservation Authority has recognised that tiger protection cannot stop at reserve boundaries.

Along with the Wildlife Institute of India, it has identified major tiger corridors across the country. These corridors are intended to guide Tiger Conservation Plans and help authorities assess the impact of development projects.

This represents an important shift from reserve based conservation to landscape level conservation.

A landscape approach examines the tiger reserve, its buffer, adjoining forests, dispersal routes, prey habitats, rivers, human settlements, and development pressures as parts of one ecological system.

The NTCA also supports scientific monitoring, management evaluation, protection forces, habitat improvement, and the use of technology for tiger conservation.

However, identifying a corridor on a map does not automatically protect it on the ground.

Corridors may include forest land, private land, revenue land, agricultural areas, and settlements governed by different departments and legal frameworks.

Effective protection therefore requires coordination between forest departments, transport agencies, mining authorities, district administrations, police, local communities, and environmental regulators.

Without such coordination, corridor maps risk becoming advisory documents rather than binding conservation tools.

Understanding the WCCB’s Role

The Wildlife Crime Control Bureau is a statutory body created under the Wildlife Protection Act.

Its primary responsibilities include collecting intelligence on organised wildlife crime, coordinating enforcement, supporting investigations, maintaining wildlife crime information, and assisting national and international action against illegal wildlife trade.

The WCCB is therefore essential for controlling poaching and trafficking, both of which threaten tigers and their prey.

However, corridor protection is not its exclusive mandate.

This distinction is important for governance analysis. The WCCB can act against wildlife crime occurring within corridors, but the legal protection of corridor land depends on several institutions.

The NTCA provides tiger conservation oversight. State forest departments manage wildlife and habitat. Environmental authorities evaluate projects. Police and district administrations support enforcement. Courts review disputes. Local bodies influence land use. Infrastructure ministries design roads and railway lines.

India does not suffer from a complete absence of institutions. It suffers from fragmented authority and uneven coordination.

A corridor may be biologically essential while remaining legally divided among agencies with competing priorities.

Lessons From the Panna Reintroduction Model

Panna Tiger Reserve offers one of India’s most important conservation lessons.

After its tiger population disappeared, tigers were reintroduced from other reserves. Intensive monitoring, protection, scientific management, and local participation helped rebuild the population.

The recovery demonstrated that extinction within a reserve can be reversed when institutions respond decisively.

But Panna also shows the limitations of focusing only on reintroduction.

Moving tigers into a reserve can restart a population. It cannot replace long term habitat connectivity.

A newly established population still requires genetic exchange, adequate prey, secure boundaries, community support, and links with adjoining landscapes.

Reintroduction should therefore be treated as an emergency recovery measure, not as a permanent substitute for ecological movement.

If India repeatedly relies on capturing and relocating tigers because natural corridors have disappeared, conservation will become increasingly expensive, risky, and artificial.

The real success of the Panna model lies not merely in moving animals. It lies in active management, monitoring, institutional accountability, and community participation.

Those lessons must now be applied to corridor conservation.

Eco sensitive zones are areas notified around national parks and wildlife sanctuaries to regulate activities that may damage protected ecosystems.

They act as transition areas between highly protected habitats and landscapes where greater human activity occurs.

These zones do not necessarily prohibit every economic activity. Instead, they classify activities as prohibited, regulated, or permitted according to their likely environmental impact.

For tiger reserves, eco sensitive zones can reduce sudden and intensive development near critical habitats.

However, an eco sensitive zone and a tiger corridor are not the same.

An eco sensitive zone generally surrounds a protected area. A corridor may connect two protected areas across a much larger landscape.

A narrow or diluted eco sensitive zone may leave important movement routes outside meaningful protection. At the same time, exemptions, boundary changes, delayed notifications, and project specific permissions can weaken the protective purpose of these zones.

The legal debate should therefore move beyond a fixed distance around reserve boundaries.

Ecological sensitivity cannot always be measured through a uniform radius. A narrow strip may be sufficient in one location and completely inadequate in another.

Scientific mapping, animal movement data, terrain, water sources, forest cover, and cumulative development pressure should guide protection.

Conservation Cannot Ignore Communities

Tiger corridors are often also human landscapes.

People may cultivate land, graze livestock, collect forest produce, travel between villages, and depend on natural resources within these areas.

Treating every corridor as an empty wilderness can produce displacement, resentment, and conflict.

Successful conservation requires incentives for coexistence.

Compensation for livestock loss must be timely. Crop damage claims should be processed efficiently. Local residents should benefit from conservation employment, tourism revenue, habitat restoration, and monitoring programmes.

Voluntary relocation from critical habitats should remain genuinely voluntary and supported by fair rehabilitation.

Communities should also be involved in identifying movement routes and conflict hotspots. Local knowledge can reveal animal paths that are missed by short term surveys.

The experience of tiger reintroduction projects shows that technical planning without community trust is unlikely to succeed.

What India Must Do Next

India should treat tiger corridors as essential ecological infrastructure.

First, identified corridors should receive clearer legal recognition within land use planning and project approval systems.

Second, every major road, railway, mining, transmission, or industrial proposal affecting a corridor should undergo a cumulative landscape assessment.

Third, wildlife crossings should be planned before construction and based on scientific evidence.

Fourth, state governments should prevent unregulated commercial development near crossing points and reserve boundaries.

Fifth, genetic monitoring should become a regular part of tiger conservation. A rising population can hide declining genetic diversity.

Sixth, compensation and community benefit systems must be strengthened across corridor landscapes.

Seventh, the NTCA, WCCB, state forest departments, infrastructure agencies, and district authorities need a permanent coordination mechanism for priority corridors.

Finally, conservation performance should not be measured only by the number of tigers photographed during an estimation exercise.

India should also measure corridor use, genetic exchange, dispersal success, conflict, habitat quality, prey density, and mortality outside reserves.

Conclusion

Rajasthan’s rise from 135 to 149 tigers is a genuine conservation achievement.

It shows that protection, monitoring, habitat management, and public investment can produce results even in a state facing considerable ecological pressure.

But the next phase of tiger conservation will be harder than the first.

Protecting tigers inside reserves is no longer enough. India must protect their ability to move between reserves.

A tiger population confined within an isolated habitat may remain stable for a period, but growing numbers cannot compensate indefinitely for lost genetic exchange, shrinking dispersal routes, and rising conflict.

The future of the tiger will therefore be decided not only in the core forests of Ranthambore, Sariska, Panna, or other reserves.

It will also be decided in the less celebrated spaces between them.

These corridors may not attract tourists or produce dramatic population statistics. Yet they determine whether India’s tiger recovery becomes a lasting ecological success or a temporary increase within disconnected islands.

Written By

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Aditi Sneha

Growth Strategist

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