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Chapter 2: The Price of the Mountain

In 2007, the Blacksmith Institute — a New York-based environmental health organisation — published a list of the world’s ten most polluted places. Alongside Chernobyl, Dzerzhinsk in Russia, and La Oroya in Peru, the list included Sukinda valley in Jajpur district, Odisha.

The reason was hexavalent chromium.

Sukinda contains ninety-seven percent of India’s chromite ore deposits, concentrated in a valley approximately twenty kilometres long. Twelve open-cast mines operated by the Odisha Mining Corporation, Tata Steel subsidiary IMFA, Balasore Alloys, and others extract millions of tonnes of chromite annually. The mining process releases hexavalent chromium — Cr(VI), a known carcinogen classified Group 1 by the International Agency for Research on Cancer — into the soil, surface water, and groundwater of the valley. Studies found chromium concentrations in local water sources exceeding WHO permissible limits by factors of twenty or more. The Damsala Nala, a stream flowing through the mining area into the Brahmani river, carried chromium-laden discharge directly into the water system that millions depend on for drinking and irrigation.

The villages surrounding the mines reported cancer clusters, skin diseases, respiratory illness, and birth defects at rates that health researchers found significantly elevated above baseline. The workers in the mines — many of them tribal — had no protective equipment and no medical monitoring. The state pollution control board documented the contamination. The National Green Tribunal issued orders. The mines continued operating.

Sukinda is not an anomaly. It is the most visible symptom of a structural condition: Odisha’s mining model treats ecological cost as an externality — a cost that appears on no balance sheet, is borne by people who have no political power, and accumulates invisibly until it produces something so undeniable that a New York organisation puts it on a global list.

The Cross-Domain Lens: Hidden Leverage

In investing, leverage is the use of borrowed capital to amplify returns. A company with 3:1 leverage makes three times the profit on the upside — and takes three times the loss on the downside. The critical danger is not leverage itself but hidden leverage: debt that does not appear on the balance sheet, obligations that are real but unaccounted, risks that are structural but unreported.

The 2008 financial crisis was, at its core, a crisis of hidden leverage. Banks had moved risk off their balance sheets into special purpose vehicles. The risk was real — the subprime mortgages existed, the default probability was calculable, the exposure was enormous — but it was invisible in the official accounts. When the hidden leverage was finally recognised, the system collapsed not because new risks appeared but because existing risks that had been invisible became visible overnight.

Odisha’s mining model operates with hidden ecological leverage. The profit that appears on the balance sheet — Rs 87,000 crore in mineral production value in 2021-22, growing at 21.4 percent annually — is real. But it is achieved by borrowing from an ecological capital base whose depletion does not appear in any government accounting. The chromium in Sukinda’s water, the deforestation in Keonjhar’s elephant corridors, the fly ash in Jharsuguda’s air, the severed streams on Niyamgiri, the subsidence in Talcher’s coal belt — these are ecological debts. They are real. They are accumulating. And like the subprime mortgages of 2007, they will eventually be recognised.

The question is not whether the ecological leverage will unwind. It is whether Odisha will manage the unwinding or be overwhelmed by it.

The Geography of Coincidence

The minerals are under the forests. The forests are on the tribal land. This is not coincidence — it is geology.

Odisha sits on two ancient geological formations: the Eastern Ghats mobile belt and the Singhbhum Craton. Together they created one of the most mineral-dense regions on the planet. Twenty-eight to thirty-three percent of India’s iron ore. Ninety-five to ninety-eight percent of its chromite. Forty-nine to fifty-nine percent of its bauxite. Twenty-four percent of its coal. Significant nickel, manganese, and graphite. The total mineral production value reached Rs 87,086 crore in 2021-22 — the highest of any Indian state — and the sector has been compounding at 21.4 percent annually.

These geological formations also created terrain — forested hills, river valleys cut through hard rock, ravines inaccessible to wheeled transport — that for millennia resisted state penetration. The minerals are under tribal land because the same geological forces that concentrated chromite and bauxite also created the topography that allowed tribal communities to maintain autonomous governance for centuries. More than fifty percent of Odisha’s tribal population resides in six districts — Mayurbhanj, Sundargarh, Keonjhar, Koraput, Nabarangpur, Rayagada — that are also the primary mineral extraction zones. Every one of these is either fully or partially a Scheduled Area under the Fifth Schedule.

The ecological implication is precise: two low-entropy systems — concentrated minerals and intact forest ecosystems — exist in the same physical space because they were created by the same geological process. Extracting one necessarily disrupts the other. There is no way to mine a mountain without disassembling the ecosystem on top of it. The Tribal Odisha series (Ch5) calls this the entropy event: mining removes the organised mineral layer and, in doing so, removes the organising principle of the ecosystem above it.

The Forest That Disappears

The most visible ecological cost of mining is deforestation.

Under the Forest Conservation Act of 1980, any diversion of forest land for non-forest purposes — including mining — requires central government approval. Odisha has been among the states with the highest forest diversion for mining. Between 2001 and 2023, tens of thousands of hectares of forest have been diverted for mining leases, access roads, overburden dumps, and processing infrastructure across the mineral belt.

The mining districts tell the story. Keonjhar, which holds the richest iron ore deposits, has seen systematic forest loss as open-cast mines expand. Sundargarh, home to both iron ore and manganese, has experienced similar degradation. Angul, the centre of coal mining, has lost forest cover to both mines and thermal power plants. Koraput and Rayagada, the bauxite belt, face deforestation from alumina refinery operations and associated infrastructure.

The compensatory afforestation mechanism — CAMPA (Compensatory Afforestation Fund Management and Planning Authority) — was designed to offset this loss. Mining companies pay into a fund; the fund finances planting of trees elsewhere to replace the forest destroyed. Odisha’s CAMPA account holds thousands of crores. But the evidence for effective compensatory afforestation is thin. Trees are planted but not maintained. Plantations are monocultures of fast-growing species (eucalyptus, teak) that bear no ecological resemblance to the mixed-species forests they replace. Plantations are sometimes established on land that was already forested, creating double-counting. And the fundamental problem persists: you cannot compensate for a complex forest ecosystem — with its soil biome, watershed function, biodiversity, and carbon stock developed over centuries — by planting saplings somewhere else. The ecological debt is real and the compensatory mechanism is, at best, a partial offset.

Satellite imagery confirms what ground surveys suggest: the forest cover in Odisha’s mining districts is declining in quality even where gross area is maintained. Dense forest is being replaced by open forest and scrubland. Canopy density is falling. Forest fragmentation — where continuous forest is broken into isolated patches by mining roads, power lines, and processing facilities — is advancing. Fragmented forests lose ecological function disproportionately to the area lost, because edge effects penetrate deep into remaining patches and wildlife corridors are severed.

The Water That Poisons

Mining’s impact on water is both immediate and persistent.

Sukinda: The Chromium Valley. The Sukinda chromite mines produce hexavalent chromium as a byproduct of extraction. Cr(VI) is water-soluble, highly mobile in groundwater, and a documented carcinogen. Studies of Sukinda have found:

  • Chromium concentrations in local water sources twenty or more times the WHO permissible limit
  • Contamination of the Brahmani river system via the Damsala Nala tributary that drains the mining area
  • Elevated cancer rates, respiratory illness, skin disease, and reproductive health problems in surrounding villages
  • Chromium in paddy fields irrigated by contaminated water, entering the food chain
  • Despite decades of documentation, no comprehensive remediation has been completed

The Sukinda case illustrates a pattern: the pollution is documented, the health impacts are studied, legal orders are issued, and the mines continue because the mineral revenue is too important to interrupt.

Acid mine drainage. When rock containing sulphide minerals is exposed to air and water — as it is in every open-cast mine — it produces sulphuric acid. This acid mine drainage dissolves heavy metals (iron, manganese, arsenic, cadmium) from surrounding rock and carries them into surface water and groundwater. AMD is particularly insidious because it continues for decades or centuries after mining ceases. A closed mine that was profitable for thirty years can produce acid drainage for three hundred.

Fly ash. Odisha’s thermal power concentration — approximately fifteen gigawatts of installed capacity, concentrated in the Angul-Talcher and Jharsuguda belts — produces millions of tonnes of fly ash annually. Fly ash ponds, some covering hundreds of hectares, leach heavy metals into groundwater. Pond breaches during monsoon can release toxic slurry into rivers. The Vedanta aluminium smelter complex in Jharsuguda, one of the world’s largest, produces both fly ash from its captive power plant and red mud from alumina processing — a caustic, alkaline waste that is stored in unlined ponds and has contaminated surrounding agricultural land.

The Lanjigarh red mud pond. Vedanta’s alumina refinery at Lanjigarh in Kalahandi district — the refinery built for the Niyamgiri bauxite that was never mined — processes bauxite brought from other sources. The refinery produces red mud, a highly alkaline waste, stored in an expanding pond system. Local communities have documented contamination of the Vamsadhara river, agricultural land damage, and health impacts. The refinery continues to operate and expand despite the bauxite mine being blocked by the Dongria Kondh gram sabhas.

The Air That Thickens

The coal dust corridor runs from Jharsuguda through Sambalpur to Angul — approximately two hundred kilometres of India’s densest concentration of coal mines, thermal power plants, and aluminium smelters.

Open-cast coal mining produces particulate matter at every stage: blasting, loading, transport, crushing, and stockpiling. The transport fleet alone — thousands of trucks carrying coal on inadequately paved roads — generates a continuous dust plume visible from satellite imagery. Add the emissions from thermal power plants (particulate matter, sulphur dioxide, nitrogen oxides, mercury) and the aluminium smelter complex (fluoride emissions, pot gas), and the result is an air quality regime that the Central Pollution Control Board has classified among the most polluted industrial clusters in India.

The health consequences are documented but poorly quantified. Silicosis — irreversible lung fibrosis caused by inhaling silica dust — is endemic among mine workers but drastically underreported because occupational health surveillance is weak and affected workers are often contract labourers with no medical records. Respiratory illness, cardiovascular disease, and cancer rates in the Angul-Talcher-Jharsuguda belt are elevated, but comprehensive epidemiological studies are scarce. The state does not conduct systematic health monitoring of populations living near mining and industrial clusters.

The Corridors That Break

Odisha’s mineral belt overlaps with critical wildlife corridors, particularly for elephants.

The elephant population in Odisha is estimated at approximately 1,900 individuals spread across forests in Keonjhar, Sundargarh, Angul, Dhenkanal, Sambalpur, and Mayurbhanj. These elephants require continuous forest corridors to move between feeding grounds, water sources, and breeding areas. Mining operations — open-cast pits, overburden dumps, processing facilities, transport roads, railway lines, and human settlements that grow around mining infrastructure — fragment these corridors.

The result is human-elephant conflict. Elephants, unable to traverse their traditional routes, enter agricultural fields and villages. Odisha reports among the highest rates of human-elephant conflict deaths in India — both human and elephant. Between 2014 and 2024, hundreds of people were killed by elephants in Odisha, and dozens of elephants died from electrocution (from illegal fences and power lines), poaching, and train strikes on railway lines that cross corridors.

Mining near or adjacent to Simlipal Biosphere Reserve (4,374 square kilometres, home to Bengal tigers and one of Odisha’s most important ecological assets), Satkosia Tiger Reserve, and Karlapat Wildlife Sanctuary adds further pressure. The 2021 Simlipal fire crisis — where fires burned through large areas of the biosphere reserve — was exacerbated by the degradation of forest buffers around the reserve’s periphery.

The ecological connectivity being severed by mining is not merely a conservation concern. It is a systems failure. Forests regulate water cycles, sequester carbon, provide non-timber forest products that sustain tribal livelihoods, buffer temperature extremes, and protect against soil erosion. When mining fragments forests, it does not just displace animals. It disrupts the ecological services that the human population depends on — the same population that the mining revenue is supposed to develop.

The Governance That Fails

Environmental governance in Odisha’s mining sector follows a pattern of formal compliance and substantive failure.

Environmental Impact Assessments (EIAs) are required before mining leases are granted. In practice, EIA quality is poor, public hearings are manipulated (documented cases of hearings held in venues inaccessible to affected communities, attendance sheets padded with non-residents, objections overridden), and clearances are granted with conditions that are never enforced. The 2020 draft EIA notification proposed further dilution — extending validity of clearances, allowing post-facto approval for violations, and reducing public participation — which environmental organisations challenged in court.

The Shah Commission found 22.80 crore tonnes of iron ore extracted illegally in Keonjhar and Sundargarh districts alone — a scam valued at over Rs 59,000 crore. Of 192 mining leases examined, 176 were within dense forests. Ninety-four lacked environmental clearances. The illegal extraction was conducted by established companies — including SAIL, Tata Steel, and the state’s own Odisha Mining Corporation — not by fly-by-night operators. The distinction between legal and illegal mining in Odisha was, for a period, effectively meaningless.

The State Pollution Control Board lacks the capacity, independence, and political backing to enforce environmental standards against mining companies that are the state’s primary revenue source. When the SPCB issues violation notices, companies obtain stays from courts. When National Green Tribunal orders are issued, compliance is delayed indefinitely. The institutional architecture for environmental regulation exists on paper. Its enforcement against the state’s most powerful economic interests is functionally absent.

The DMF paradox. The District Mineral Foundation, created in 2015, collects a levy from mining companies and is supposed to spend it on development in mining-affected areas. Odisha has the largest DMF collection in India — over Rs 23,000 crore cumulative. This is an enormous resource. But DMF spending patterns reveal the paradox: funds are disproportionately allocated to infrastructure (roads, buildings) rather than environmental remediation, health monitoring, or ecosystem restoration. In documented cases, DMF funds have been diverted to purposes unrelated to mining impact — Sundargarh DMF money was used to purchase police patrol vehicles for Rourkela city, which is not a mining-affected area. The fund designed to address mining’s ecological cost is not being used to address mining’s ecological cost.

The Time Scale of Damage

The temporal dimension of ecological damage from mining is the dimension most consistently ignored.

An open-cast mine operates for twenty to fifty years. The ecological damage it causes persists for centuries. Acid mine drainage from abandoned mines continues for three hundred years or more. Deforested land in tropical conditions takes fifty to one hundred years to regenerate anything resembling the original ecosystem — and only if left undisturbed, which it never is. Hexavalent chromium in groundwater persists indefinitely without active remediation. Heavy metals in agricultural soil remain bioavailable through multiple crop cycles.

Mine closure plans are required by Indian mining regulations. In practice, most closure plans exist on paper and are never implemented. When a mine’s lease expires or the deposit is exhausted, the pit, the overburden dump, the tailings pond, and the contaminated water table are typically abandoned. Reclamation — filling the pit, grading the overburden, treating the water, replanting vegetation — costs a fraction of what the mine earned during operation but is rarely budgeted because the mining company has moved on and enforcement is absent.

The result is a growing stock of ecological liabilities across Odisha’s mineral belt — abandoned mines, contaminated aquifers, degraded forests, severed corridors, polluted rivers — that will require remediation for decades or centuries after the mineral revenue has been spent.

In investing terms, this is a company that reports profit every quarter while its actual liabilities — off-balance-sheet, unaccounted, growing — quietly exceed its net worth. The quarterly earnings look strong. The enterprise is insolvent and doesn’t know it.

The Double Extraction

The Value Chain series (Ch1-Ch2) documents how Odisha captures roughly ten percent of the value its minerals generate — the other ninety percent accrues to processing and manufacturing that happens in other states. Tribal Odisha Ch5 documents how the minerals under tribal land are extracted with inadequate compensation, broken rehabilitation promises, and systematic violation of PESA and FRA protections.

The environmental lens reveals a third layer of extraction. Odisha’s mining model extracts not only the mineral (the obvious extraction) and the economic value (the value chain extraction) but also the ecological capital — the forests, water systems, soil quality, biodiversity, and atmospheric quality that sustain the population living above the minerals.

This triple extraction — mineral, economic, ecological — means that for every tonne of iron ore shipped from Keonjhar to Jamshedpur, Odisha loses not only the ore and the processing value but also a quantum of forest cover, water quality, air quality, and ecological resilience that no royalty or DMF levy compensates. The Rs 87,000 crore mineral production value is offset by ecological losses that have never been quantified because no one has been asked to quantify them.

The closest estimate comes from ecosystem services valuation frameworks — the TEEB (The Economics of Ecosystems and Biodiversity) approach that assigns monetary value to services like carbon sequestration, water filtration, flood regulation, and biodiversity maintenance. Applied to India’s forests, these valuations consistently find that the ecosystem services value of standing forest exceeds the one-time extraction value of the minerals beneath it. The forest that filters water for a million people provides that service every year, in perpetuity. The iron ore extracted from beneath it provides revenue once.

But ecosystem services valuation is academic. It does not appear in Odisha’s budget. It does not influence mining lease decisions. It does not feature in election campaigns. The hidden leverage continues to accumulate because the accounting system was designed to make it invisible.

Niyamgiri: The Road Not Taken

The Niyamgiri case, documented in Tribal Odisha Ch5, is analytically important not just as a tribal rights story but as the one instance where the ecological cost of mining was weighed against the economic benefit — and the ecological cost won.

The twelve gram sabhas in 2013, all voting unanimously against mining, were responding not only to cultural and religious concerns but to ecological reality. The Niyamgiri bauxite deposit sits atop a plateau whose geological structure functions as a hydrological sponge — porous aluminium hydroxide absorbing monsoon rainfall and releasing it gradually through over three hundred perennial streams feeding the Vamsadhara and Nagavali river systems. Remove the bauxite and the sponge disappears. The streams dry. The forest, deprived of its hydrological substrate, dies from the roots up. The plains below lose their water source.

The Dongria Kondh understood this — not in geological vocabulary but in the practical knowledge of people whose livelihood depended on the streams. Their “no” was, among other things, an ecological assessment: the long-term value of the mountain’s water function exceeded the short-term value of its bauxite.

The irony is that Vedanta’s alumina refinery at Lanjigarh was built anyway, and operates on bauxite sourced from elsewhere. The red mud pond grows. The Vamsadhara carries its pollution. The mountain was saved but the refinery’s environmental damage continues. Niyamgiri showed that ecological cost can, in principle, be recognised. It did not show that ecological cost can, in practice, be prevented.

What the Balance Sheet Does Not Show

Here is the environmental balance sheet that no government publishes:

Revenue side (what Odisha captures):

  • Rs 22,000-29,000 crore annually in mining revenue (2023-24)
  • Rs 23,000+ crore cumulative DMF collection
  • Employment for approximately 150,000-200,000 workers
  • Contribution to approximately 84 percent of non-tax revenue

Cost side (what Odisha loses):

  • Tens of thousands of hectares of forest diverted
  • Hexavalent chromium contamination in Sukinda valley — duration: indefinite
  • Heavy metal contamination across mining districts
  • Fly ash and red mud accumulation — millions of tonnes, growing annually
  • Severed elephant corridors and accelerating human-wildlife conflict
  • Brahmani and Baitarani river pollution affecting downstream agriculture and fisheries
  • Air quality degradation across the coal dust corridor
  • Acid mine drainage from abandoned mines — duration: centuries
  • Carbon release from deforestation — contributing to the climate change that produces the cyclones OSDMA manages

The revenue side appears in the state budget. The cost side appears nowhere.

This is the hidden leverage. It is real. It is growing. And when it unwinds — through water crises, health emergencies, ecosystem collapse, climate penalties like the EU’s Carbon Border Adjustment Mechanism — the bill will arrive all at once, the way it always does with hidden leverage. The prior series asked why Odisha’s mining wealth has not produced industrial transformation (Value Chain) or institutional development (The Long Arc). This chapter asks a different question: even the mining wealth that Odisha does capture may be less than the ecological capital it destroys to capture it. The profit may be an illusion maintained by not counting the cost.

Sources

  • Blacksmith Institute / Pure Earth, “The World’s Worst Polluted Places” (2007)
  • Shah Commission of Inquiry on Illegal Mining in Odisha (2013-14)
  • National Green Tribunal orders on Sukinda chromite mining
  • Central Pollution Control Board, Environmental Quality Monitoring Data
  • Forest Conservation Act, 1980; CAMPA guidelines
  • MMDR Amendment Act, 2015 (DMF creation)

Prior SeeUtkal Series

  • Tribal Odisha Ch5 (The Mountain and the Mine): Niyamgiri, Kalinganagar, entropy framework, mineral-tribal overlap
  • Value Chain Ch1-2 (The Tonne’s Journey, The Value Staircase): per-tonne economics, 90/10 value split, government take comparison
  • The Long Arc Ch5 (The Extraction Equilibrium): mining revenue, Nash equilibrium, welfare architecture
  • Delhi’s Odisha Ch3 (Who Keeps the Money): MMDR Act, royalty history, DMF

Research and Academic Sources

  • IBM (Indian Bureau of Mines), Odisha State Mineral Report
  • Odisha Economic Survey 2024-25
  • Government of Odisha, Department of Steel and Mines
  • Heinrich Boll Foundation, “Mahanadi: Coal Rich, Water Stressed” (2018)
  • Mongabay India, DMF utilisation investigation (2021)
  • CSE India, DMF fund analysis
  • TEEB (The Economics of Ecosystems and Biodiversity) India initiative

News Sources

  • Down to Earth, Sukinda chromite contamination coverage
  • OdishaBytes, mining and environment reporting
  • Business Standard, mining sector data
  • Mongabay India, “Sundargarh DMF funds diverted to police vehicles”

Source Research

The raw research that informs this series.