Rewilding Gujarat: Returning Native Herbivores to Restored Forests

Australia knows what it means to put animals back on land that once carried them. From the feral-proof fences of the Australian Wildlife Conservancy to community-driven refuges near Renmark, the continent has spent decades refining what ecologists now call rewilding. In Gujarat, forest managers are running a parallel experiment, focused on ungulates that vanished from many landscapes during the twentieth century. The plan blends ecological science, village participation and a long-running state forest department with one clear goal: rebuild habitat first, then return native herbivores so each system can carry a full complement of species.

Gujarat spans semi-arid thorn scrub in Kutch, dry deciduous forests around Dahod and Chhota Udepur, and moist teak-bearing ranges on the edge of the Dang. Across this mosaic, ungulates once shaped the grass layer, kept acacias in check and provided the prey base for leopards, wolves and the world's last free-ranging population of Asiatic lions in Gir. Decades of livestock pressure, drought, mining expansion and canal-driven fragmentation pushed several native herbivores into isolated pockets. Where they disappeared, grass fires burned hotter, saplings failed to recruit, and smaller predators turned to livestock. Reversing that spiral is the thread tying the new strategy together.

Herbivores are ecosystem engineers. Blackbuck and chinkara crop grasses and forbs to maintain the open structure favoured by ground-nesting birds, while sambar and four-horned antelope browse the shrub layer and disperse seeds of several tree species. When grazing and browsing pressure is removed for too long, fuel loads build, fire regimes shift and woodland composition drifts. The Gujarati programme treats herbivore reintroduction as a way to restore a missing ecological function, not as a publicity exercise.

The work is staged carefully. Degraded blocks within the protected area network are rehabilitated through native grass seeding, controlled grazing rest, water-point engineering and invasive species removal. Only after a site meets measurable vegetation, water and prey-base thresholds are founders translocated from source populations elsewhere in the state or from selected captive stocks. Monitoring continues for years with radio-collars, camera traps and field surveys feeding back into adaptive management plans. The model borrows from international translocation guidelines while keeping decisions with local forest officers who know the terrain.

Why Herbivore Reintroduction Sits at the Centre of the Plan

Few ecological interventions carry the visual power of an antelope stepping onto ground it has not occupied for a generation, yet emotion is not the driver. Internal assessments point to cascading benefits: more diverse grass swards, healthier fire intervals, stronger prey populations for large carnivores, and richer ecotourism opportunities. Where chinkara have been monitored after release, browse lines on certain acacias have stabilised, suggesting that the animals are filling a niche left empty for decades.

The argument also carries an economic edge. Pastoral communities around Banni, Velavadar and the edges of Gir have watched grass cover shrink as commercial grazing expanded. By restoring native grazers and managing livestock through regulated permits, the state hopes to reduce conflict over forage and give village cooperatives a stake in keeping the landscape productive. Australian readers who follow banteng recovery at Mareeba Tropical Savanna and patch-burn projects across the Top End will recognise the same logic. Reintroducing a wild herbivore is rarely just about the animal.

Choosing the Right Species for the Right Landscape

Not every species is suitable for every site, and the strategy is explicit about that. In the dry thorn forests of Kutch and northern Saurashtra, chinkara and a small number of blackbuck are the priority. In the central mixed-teak forests of the Dang and around Shoolpaneshwar, sambar and four-horned antelope (chowsingha) feature higher on the list. Wild water buffalo are being considered for the wettest habitats, while Indian gazelle is on the radar for grass-rich enclosures near the Pakistan border. Each pairing matches soil, rainfall and current vegetation.

Genetic considerations shape these choices too. The state forest department is working with the Wildlife Institute of India and several zoos, including the Werribee Open Range Zoo near Melbourne, to identify source populations with adequate genetic diversity and avoid inbreeding depression in founding groups. IUCN guidelines recommend a minimum effective population size for translocations, and Gujarati planners have built those thresholds into site selection. The result is a species-by-species matrix rather than a one-size-fits-all release schedule.

Rebuilding Habitat before the First Animal Arrives

Release without preparation is a recipe for failure, and the state has invested heavily in pre-release habitat work. Forest teams are removing Prosopis juliflora, an invasive tree that has overtaken thousands of hectares of grassland, and replacing it with native species such as Acacia nilotica and locally sourced grasses. Water is the limiting factor, so small check dams, percolation tanks and seasonal water points have been added in clusters designed to mimic natural drainage lines.

Fire management is the other pillar. Long fire-free intervals were allowing woody species to invade open grasslands, making them less attractive to grazers. Controlled cool burns, timed with the advice of local livestock keepers, are now lighting up selected patches each year. Similar approaches have been refined across northern Australia, where fire-stick farming practised by Aboriginal communities for tens of thousands of years shapes contemporary savanna management in the Kimberley and Cape York. The Gujarati version adapts the principle to drier, more fragmented terrain.

Sourcing, Translocating and Releasing with Care

Once a site passes habitat criteria, the focus shifts to the animals themselves. Source populations are screened for disease, parasites and genetic profile. Capture is carried out under veterinary supervision, often using drive nets and small corral traps set up near water. Animals are kept in soft-release enclosures for several weeks at the destination site, given supplementary forage and water, and fitted with satellite or VHF collars before the gate is finally opened. The approach mirrors protocols used in eastern bettong returns to mainland sanctuaries in New South Wales and Victoria.

Field teams are trained in welfare-focused handling, with stress indicators tracked through faecal cortisol samples and behavioural scoring. Hard releases are reserved for hardy species with wide historical ranges, while soft release is the default for anything considered vulnerable. Survival data from the first cohort at a trial site in central Gujarat suggest that soft-released chinkara showed lower dispersal distances and higher short-term survival than animals released directly. That kind of feedback loop is shaping protocols as the programme expands.

Communities, Pastoralists and the Wider Landscape

No reintroduction survives without local support, and the state has leaned on village forest committees, joint forest management groups and eco-development committees around protected areas. Pastoralists are brought into planning from the start, with grazing rights, water access and compensation for crop damage negotiated before any animal is moved. These negotiations are rarely straightforward. The honest assessment from field staff is that progress is uneven, with the strongest uptake in the Banni region and the most resistance along the boundary of newer tiger-bearing habitats further east.

Australian parallels are worth noting. Across the pastoral leases of western Queensland and the Kimberley, station managers face similar trade-offs when feral herbivores such as donkeys, camels or pigs are replaced with native species under controlled conditions. The EPBC Act sets a national framework for translocation approvals, with state-level wildlife regulations adding another layer. Gujarat's equivalent stack includes the Wildlife (Protection) Act of 1972, state forest rules and National Tiger Conservation Authority guidelines.

Monitoring, Protection and the Road Ahead

Protecting the new populations once they are out in the landscape is as important as putting them there. Camera traps cover release sites at densities that would have been impossible a decade ago, feeding into long-term population models. Anti-poaching work has gone high-tech too, with the state forest department increasingly relying on drone-based anti-poaching patrols to cover vast blocks in less time. Drones can spot vehicles on forest roads at night and direct ground teams to incidents before they escalate.

The next phase will look beyond individual sites to corridors, linking reintroduction zones with larger forest complexes through habitat-friendly land use, voluntary conservation easements and partnerships with non-profits. Funding will come from a mix of state budgets, central government schemes and bilateral conservation grants. Readers keen to see how these threads fit into the wider story can explore the state's wider forest programme, which covers everything from mangrove rehabilitation to urban tree planting. Visit the page, share it with a colleague, and follow a project that is quietly showing what patient, science-led habitat work can deliver for wildlife and people.