Solar Park on Charagah: Renewable Targets and a Great Indian Bustard Breeding Area

Step 1 - avoid. The first question is not how to make 1,200 ha acceptable, but whether this 1,200 ha is needed. 'Waste land' is an administrative revenue category, not an ecological description: the presence of three nests in the adjoining grassland and a functioning nadi means the site is habitat, and the 11 families' use means it is productive commons. Avoidance requires asking whether alternative land - truly degraded, already fenced, farther from the breeding area - is available within the transmission corridor. If the developer selected this site for its cheap lease, avoidance is feasible.

Step 2 - minimise, if avoidance fails. 6 km from a breeding area with three recorded nests is not a trivial distance for a large, low-flying, display-dependent bird. Micro-siting matters: keep the array out of the sightline between nest sites and the nadi, retain an unfenced buffer of a few hundred metres around the nadi, avoid night lighting, and keep all cabling underground - the proposed 33 kV underground line is the single best feature, because collision with overhead lines is a principal mortality factor for the species, and courts have pushed for undergrounding in its habitat.

Step 3 - restore and offset are the weakest tools. Grassland restoration around a solar park is unreliable and slow; an offset of ₹2 crore cannot recreate a breeding site.

Weighing it: 300 MW is significant but a national target is met by many projects, whereas the species has very few breeding locations left. If the site is inside or adjoining a legally protected area or its eco-sensitive zone, the collector is not the competent authority at all - wildlife clearance is required, and that should be checked before anything else.

Verdict: refuse unconditional diversion; permit a redesigned, micro-sited, unfenced project only if independent biological clearance is obtained and the nadi and grazing corridor are retained. The answer would change if the nesting records were one-off and no nesting is confirmed in a second season.

Underground 33 kV line - reduces harm, keep it. Collision with overhead power lines is a leading mortality factor for large grassland birds; burying the collector line removes that risk entirely. This is the element to insist on in writing, along with a ban on new overhead lines within the site.

2.5 m chain-link fence - increases harm, remove or redesign. For a bird that needs open sightlines and for chinkara and grazing livestock, a full perimeter fence is a barrier that fragments the grassland, separates animals from the nadi, and creates entanglement and perching hazards. It also converts a commons into an enclosure, which is the mechanism by which pastoral access is lost without any formal decision. Substitute: no perimeter fence around the array, or wildlife-permeable fencing (low, large-mesh, gapped at known movement corridors) around only the inverter and substation compounds.

Panels at 1.8 m - mixed, depends on layout. Higher mounting allows some movement underneath and preserves grass, but a dense field of panels and their shadow still displaces bustards, which avoid vertical structures and shaded, cluttered ground. Height alone is not mitigation; spacing, row orientation, the size of the cleared area, and the distance from the nadi matter more. Substitute: cluster the array, leave large contiguous open patches, keep the nadi and its approach flight lines clear, and forbid night floodlighting.

Add what is missing: a dust-suppression and panel-cleaning water plan (water is the scarcest resource here), a ban on rodenticide and on free-ranging dogs attracted by workers' waste, and a bird-monitoring protocol with an independent observer for the first three years.

Judgement rule: any design feature that increases the number of vertical structures, lights, water demand or fences in the breeding season should be justified explicitly - the default should be the least cluttered layout, not the cheapest one.

What the offer gets wrong

• It treats commons as a cash transaction. Charagah is held for community grazing, not as individual property. Paying compensation to a group does not recreate grazing, water or the customary routes that make a pasture usable. Cash is spent; the nadi is not.
• The replacement may not be equivalent. A grazing reserve 'elsewhere' needs its own water source (a tanka or nadi), a size that supports 400 goats and 60 camels, and access rights that are recorded so they cannot be reallocated later. Without these, the offer is a promise.
• Twenty jobs is not a livelihood for eleven families, and construction jobs are temporary. Herding is a skill with no substitute in the labour market.
• ₹2 crore without a delivery mechanism has no accountability: who holds it, who audits it, and what happens if the reserve is not developed?

A fairer process

1. Verify land records and identify every user, including landless herders and women, who are often invisible in settlement lists.
2. Consult through the Gram Panchayat and a recorded Gram Sabha, with documents in the local language, before the diversion decision - not after the lease is signed.
3. Prefer land for land: identify and legally record an alternative grazing area with water, before the project starts.
4. Retain access to the nadi and to movement corridors through the site, written into the lease conditions and monitored.
5. Put the money in a panchayat-managed pasture development fund with a published plan (water harvesting, grass seed, protection), audited annually.
6. Create a grievance mechanism with a named officer, and make the developer's compliance report public.

The judgement point: the collector's duty is not to maximise the payment but to ensure that the resource base - grass, water, mobility - is not diminished. If it is, the project has failed the sustainability test regardless of the cheque.