38,552 Hectares: Madhya Pradesh Led India in Forest-Land Diversion. Was the Price Worth It?
The paper forests of Madhya Pradesh: inside India's largest land-diversion machine — and the gap between what is approved on paper and what happens to forests, hills, wildlife corridors and communities on the ground.
Across a ten-year span from 2014–15 to 2023–24, Madhya Pradesh accounted for 38,552.61 hectares of forest land approved for non-forestry use — more than any other state in India.
According to data submitted by the Ministry of Environment, Forest and Climate Change (MoEFCC) to Parliament, the national total of approved forest diversion stood at 1,73,396.87 hectares. Madhya Pradesh alone accounted for 22.23% — more than one-fifth of all forest land authorised for diversion across the country.
Odisha followed at 24,458.89 hectares and Telangana at 11,422.47 hectares.
Behind these administrative approvals lies a more complicated reality: a gap between what is signed on paper in Bhopal and New Delhi and what ultimately happens to trees, hills, wildlife corridors, water systems and landscapes on the ground.
Primary parliamentary source: Lok Sabha Annexure to Starred Question No. 333, answered March 24, 2025 .
Approval vs. felling: the first strategic gap
The parliamentary figure of 38,552.61 hectares represents forest land approved for non-forestry use under the forest-conservation regime. It is the scale of land authorised for a change of use; it is not a satellite-derived measurement of the area physically clear-felled during those ten years.
That distinction is essential. Large projects are frequently executed in phases. A highway widening, mining operation, transmission line or irrigation project can obtain approval for a defined forest area while construction and actual tree removal occur over different periods.
Stage-I and Stage-II approvals are recorded through the forest-clearance system, while project-level execution involves state departments, forest divisions and implementing agencies. The critical accountability question is therefore whether the final ground footprint corresponds with the approved footprint and whether all attached conditions were actually implemented.
A road may occupy only a relatively narrow strip on a map while nevertheless fragmenting a wildlife corridor. An open-cast mine may have an approved lease area while haul roads, dumps, drainage changes, stockpiles and associated infrastructure alter the surrounding landscape.
- Proposal area
- Stage-I approval
- Stage-II approval
- Conditions attached to clearance
- Compensatory-afforestation obligations
- Actual trees removed
- Actual construction footprint
- Habitat fragmentation
- Changes to drainage and soil
- Wildlife movement and disturbance
What Parliament's data actually establishes
The Union government's parliamentary data gives a clear state-level comparison. Madhya Pradesh stands first, followed by Odisha and Telangana.
Bars are indexed to Madhya Pradesh's official parliamentary total. They are a visualisation of the government figures, not a separate dataset.
| State | Forest land approved | Share of India's total |
|---|---|---|
| Madhya Pradesh | 38,552.61 ha | 22.23% |
| Odisha | 24,458.89 ha | 14.11% |
| Telangana | 11,422.47 ha | 6.59% |
| Gujarat | 9,985.15 ha | 5.76% |
| Arunachal Pradesh | 9,495.98 ha | 5.48% |
| India | 1,73,396.87 ha | 100% |
Source: Rajya Sabha parliamentary record, August 8, 2024 , and Lok Sabha Annexure, March 24, 2025 .
Geometry of loss: where the hectares matter
In Central India's tiger landscape, the location of a diverted hectare can matter more than the number itself.
A hectare in an already fragmented landscape is not necessarily equivalent to a hectare forming part of a wildlife corridor. A quarry beside an urban settlement is a different ecological proposition from an open-cast mine inside a forested landscape. A road through a heavily used wildlife movement route can create effects that extend far beyond the width of the road.
Source / methodology: Author's analysis compiled from project-clearance data on the PARIVESH Portal of the Ministry of Environment, Forest and Climate Change, Government of India, cross-referenced with Stage-II forest-clearance filings under the Van (Sanrakshan Evam Samvardhan) Adhiniyam, 1980, for the 2014–2024 period. These approximate percentages are an analytical classification and should not be confused with an official MoEFCC sector-wise parliamentary table.
The forest question becomes a wildlife question
Madhya Pradesh's forests do not exist as isolated green islands. They form part of one of India's most important tiger landscapes. That is where the forest-diversion number becomes more than a land-record statistic.
The National Tiger Conservation Authority and the Wildlife Institute of India have identified major tiger corridors across the country. Connectivity matters because animals need to move between habitat patches to maintain viable populations.
NTCA's work on Central India describes a landscape where fragmented habitats face developmental pressure, including mining and linear infrastructure such as roads and other transport corridors.
The Kanha–Pench corridor, for example, connects important tiger populations through Madhya Pradesh's forest landscape. Such corridors are used not only by tigers but also by leopards, dholes, gaurs and other wildlife.
The Satpura–Pench landscape presents another connectivity challenge, with agriculture, settlements and infrastructure contributing to fragmentation.
This is why corridor analysis must accompany acreage analysis. Not every diverted hectare lies inside a tiger corridor, and not every development project produces the same ecological effect. But fragmentation can turn a connected landscape into disconnected habitat even when large patches of forest remain on both sides.
Evidence: NTCA corridor-management framework , Status of Tigers and Co-predators in India, 2022 , and Connecting Tiger Populations for Long-term Conservation .
The forest-diversion debate is often framed around major tiger reserves, large dams or nationally significant mines. But the environmental cost of extraction can also be observed much closer to cities.
Around Sanawadiya village and Kathotian hill, researchers used high-resolution satellite imagery and GIS to assess changes associated with basalt quarrying. The study compared imagery from 2000 through 2015.
The researchers reported a substantial expansion in the mapped quarry footprint and associated land degradation, including changes in topography and hydrological conditions.
This is not evidence that Sanawadiya forms part of the 38,552.61-hectare parliamentary forest-diversion total. It is a separate local case study demonstrating how extraction can physically reshape a landscape over time.
Government records also document recent stone-mining clearance activity in Sanawadiya. A 1.30-hectare stone-mine proposal associated with village Sanawadiya received environmental clearance in May 2024.
Research: Assessment of Land Degradation Due to Opencast Mining Using Remote Sensing and GIS . Government record: MP SEIAA application status .
The cost of restoration: Shankargarh's lesson
Shankargarh Hills in Dewas provides another way to understand the long tail of landscape damage.
Proceedings before the National Green Tribunal describe Shankargarh as a landscape that was restored after extensive mining activities. The litigation also concerned the future status and protection of the regenerated forest and biodiversity landscape.
The NGT material placed the restored area at approximately 83 hectares. A later proceeding concerned approximately 50.292 hectares of the restored Shankargarh Nagar Van and Biodiversity Park that had been proposed for transfer for non-forest commercial purposes.
The case is significant because it demonstrates both sides of environmental restoration: damaged land can recover, but recovery requires years of protection, planting, maintenance and institutional attention.
Restoration should therefore not be treated as proof that the original ecological system has simply been recreated. A regenerated park can be valuable while still being ecologically different from the mature landscape that preceded mining.
Official judicial material: National Green Tribunal Joint Committee Report in OA No. 37/2025 (CZ) . See also the National Green Tribunal case material .
Ken–Betwa: development versus ecological accounting
The Ken–Betwa Link Project illustrates why the forest question cannot be reduced to a simple argument between “development” and “no development”.
The project has stated irrigation and water-supply objectives and involves a large network of infrastructure. Project documents available through the government's PARIVESH system identify substantial land requirements for different components, including forest land.
The appropriate environmental questions are therefore specific: What habitat is lost? What wildlife movement is affected? What mitigation is implemented? Where is compensatory land created? And do those measures reproduce meaningful ecological functions?
Those questions become particularly important in Central India's tiger-bearing landscape, where connectivity between protected areas matters alongside the protection of individual reserves.
Project documentation: PARIVESH, Ministry of Environment, Forest and Climate Change .
The compensatory-afforestation mirage
When forest land is diverted, the regulatory system relies on compensatory measures funded through mechanisms including CAMPA. But “planting trees somewhere else” and “replacing a forest” are not automatically the same ecological proposition.
- Young saplings
- Often uniform age structure
- Developing canopy
- Limited early habitat complexity
- Dependent on maintenance
- Multiple tree ages
- Complex understory
- Mature canopy
- Established soil ecosystem
- Food webs and wildlife movement
Age and complexity
A young plantation of uniform saplings cannot immediately replicate an established forest with mature canopy, understory vegetation, soil layers, nesting sites, water-retention functions and established food chains.
Geographic disconnect
Compensation located far from the original forest may satisfy an administrative requirement without restoring the ecological function that was lost at the original location. A plantation cannot reconnect a severed wildlife corridor simply because it exists elsewhere.
Long-term survival
Initial plantation numbers also do not automatically demonstrate long-term ecological success. The meaningful questions are survival after several years, canopy development, regeneration, soil and water recovery, protection from grazing or fire, and whether wildlife actually uses the restored landscape.
The compliance question is as important as the clearance
Every forest clearance comes with conditions. The existence of a condition on a clearance letter, however, does not by itself prove that the condition was carried out effectively on the ground.
The government's PARIVESH platform creates an important transparency opportunity. Proposal documents, status information and clearance records can be examined online.
But transparency is most useful when records can be connected from beginning to end: proposal → approval → forest area → trees affected → conditions → compensatory land → payment → plantation → compliance → inspection → final status.
That chain is what the public needs to reconstruct project by project.
Official portal: PARIVESH .
What the project files reveal
Individual forest-clearance records show why the aggregate number must eventually be unpacked proposal by proposal.
For example, a forest-clearance timeline for the Bangwar underground mine in Shahdol records 36.734 hectares of forest land proposed for diversion. Another proposal for the Sahapur West Coal Mine records approximately 80.590 hectares of forest land.
These individual files are not presented as representative of the entire 38,552.61-hectare total. They illustrate the level at which the real investigation must ultimately operate.
Government forest-clearance records: Bangwar UG Mine — 36.734 ha and Sahapur West Coal Mine — 80.590 ha .
The “peak year” problem: why annual numbers need a source trail
A year-by-year table has circulated alongside the 38,552.61-hectare state total, including a claim that Madhya Pradesh recorded 6,352.10 hectares in 2020–21.
That number should not be presented as an official parliamentary annual figure unless it can be reproduced from the underlying MoEFCC annual dataset or a corresponding parliamentary annexure.
The parliamentary documents used here establish the ten-year state total and the national total for April 1, 2014 to March 31, 2024. They do not, in the cited annexure, provide the ten separate annual Madhya Pradesh figures in the circulating table.
Requires separate proposal-level verification: sector-wise acreage; actual physical felling; exact Stage-II totals; CAMPA deposits; compensatory-afforestation land executed; plantation survival rates; and individual project acreage attributed to particular companies or corporate groups.
So, was it worth it?
There is no honest way to answer that question by looking at the 38,552.61-hectare figure alone.
Some projects can deliver benefits that are real and measurable. Irrigation can increase agricultural productivity. Roads can connect communities and markets. Electricity infrastructure can improve reliability. Strategic infrastructure can serve public purposes that cannot simply be relocated to avoid every forest patch.
But those benefits do not make every hectare interchangeable with every other hectare. Nor does a project's economic value erase the ecological cost of the landscape it occupies.
The appropriate comparison is therefore not simply “development versus trees”. It is:
If a road saves hours of travel but creates a barrier through a wildlife corridor, mitigation and ecological consequences belong in the accounting.
If a mine generates employment and revenue but removes a hill, changes drainage and fragments habitat, those costs also belong in the accounting.
If a dam delivers irrigation but submerges forest, compensation must be judged by what actually replaces lost ecological functions — not merely by the number of saplings planted elsewhere.
What the evidence says about the after-effects
The evidence assembled here does not support a simplistic claim that every hectare diverted has produced the same damage. It supports something more useful: forest loss and landscape alteration can create effects larger than the area directly excavated or built upon.
NTCA's corridor assessments demonstrate why. A road, railway or mine can fragment habitat and interfere with movement between otherwise connected forest patches. Wildlife-friendly linear infrastructure, including crossings and other mitigation structures, can reduce some of these effects — but only when properly designed, located and maintained.
The Sanawadiya study demonstrates another dimension. Over the period examined, the mapped quarry footprint expanded substantially around Kathotian hill, with researchers associating mining with land degradation and changes in topography and hydrological conditions.
Shankargarh demonstrates what happens when the environmental conflict continues into the legal system. Mining can stop, restoration can begin, and years later regulators and courts may still be deciding how the regenerated landscape should be classified and protected.
These are three different pieces of evidence from three different contexts. They should not be merged into one statistic. Together, however, they show why the 38,552.61-hectare number needs to be followed by another set of numbers: project by project, district by district and landscape by landscape.
What should the public be able to see?
These are not anti-development questions. They are accountability questions.
Madhya Pradesh's position at the top of the national forest-diversion table is therefore not an achievement to celebrate or condemn without context. It is a number that demands scrutiny.
The state has a large forest estate and some of India's most important tiger landscapes. That makes the quality of every diversion decision more important, not less.
How this investigation should be read
This investigation deliberately separates verified parliamentary figures from claims that require proposal-level checking.
The official ten-year total is used as the baseline. Wildlife impacts are supported with NTCA/WII assessments. Sanawadiya is treated as a documented local mining case study rather than being folded into the forest-diversion total. Shankargarh is used as a documented example of the longer environmental and legal consequences associated with mining and landscape conversion.
The sectoral percentages presented in this article are explicitly labelled as author's analysis based on project-level clearance records. They are not represented as a direct official parliamentary sector table.
This distinction matters because environmental reporting becomes weaker when estimates, approvals, actual clearing and ecological damage are treated as if they were the same thing.
Sources and official records
1. Parliament of India — Lok Sabha. Annexure to Starred Question No. 333, “Diversion of Forest Land for Developmental Activities”, March 24, 2025 .
2. Parliament of India — Rajya Sabha. Parliamentary record, August 8, 2024 . The record identifies 1,244 proposals and 38,552.61 hectares for Madhya Pradesh for April 1, 2014 to March 31, 2024.
3. MoEFCC / PARIVESH. Official PARIVESH portal for environmental, forest and wildlife clearance records.
4. NTCA. Tiger corridor management framework .
5. NTCA / WII. Status of Tigers and Co-predators in India, 2022 .
6. NTCA / WII. Connecting Tiger Populations for Long-term Conservation .
7. Sanawadiya research. Assessment of Land Degradation Due to Opencast Mining Using Remote Sensing and GIS .
8. Madhya Pradesh environmental clearance records. MP SEIAA application status .
9. Shankargarh. National Green Tribunal Joint Committee Report in OA No. 37/2025 (CZ) .
10. Individual forest-clearance records. Bangwar UG Mine and Sahapur West Coal Mine .
Author: Tina Khatri — official portfolio, books and journalism work .