When governments design policies to reduce poverty and boost livelihoods, the intention is usually good. But in fragile ecosystems – drylands, coastal zones, semi-arid regions – these same policies can trigger a cascade of environmental damage that ultimately deepens the poverty they were meant to solve. From subsidised electricity driving groundwater depletion to water-guzzling cash crops replacing climate-appropriate millets, India offers some of the clearest examples of how shortsighted policy can undermine both ecology and economy.

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How well-meaning subsidies fuel resource over-exploitation

Government subsidies are powerful tools. They can make farming affordable, put food on tables, and lift communities out of poverty. But when subsidies are offered without considering the ecological limits of a region, they can push resource use far beyond what the environment can sustain.

Since the 1960s, India’s support for the Green Revolution increased demand for groundwater in agriculture. Rapid rural electrification, combined with modern pump technologies, led to a dramatic rise in borewells – from about 1 million to 20 million over the last 50 years. The mechanism was straightforward: state governments offered free or heavily subsidised electricity for pumping groundwater, making irrigation cheap and accessible even in water-scarce areas.

The result? Groundwater is now being extracted much faster than it can be replenished. According to the World Bank, around 60% of India’s districts are likely to reach critical levels of groundwater depletion within two decades. The Central Groundwater Board estimates that roughly 17% of groundwater blocks in India are already overexploited, while another 5% are at critical and 14% at semi-critical stages.

Similarly, cheaper credit for purchasing livestock – offered to support pastoral livelihoods – can lead to overstocking and overgrazing, particularly in semi-arid and arid pastures where vegetation recovery is naturally slow. These fragile grasslands, once degraded, take decades to regenerate.

The perverse incentive loop

The problem with many of these subsidies is that they create what economists call perverse incentives. When governments initially subsidise investments in groundwater irrigation to expand farming and reduce poverty, and these subsidies are not removed once irrigation takes off, they can quickly turn counterproductive – driving individual users into a competitive race to drill ever deeper wells. Several states with depleting groundwater continue to provide free or subsidised power – including solar pumps – for irrigation, enabling the very overexploitation they should be controlling.

The research published in Nature Communications makes this link explicit: the government’s food procurement system led to significant changes in regional cropping patterns away from traditional crops suited to local climate and soil. To support these shifts, state governments offered subsidised electricity for pumping groundwater, which in turn caused widespread depletion.

Water-intensive crops in water-scarce regions

One of the most visible policy failures in fragile ecosystems is the promotion – or at least tolerance – of crops entirely unsuited to local rainfall and soil conditions. Sugarcane is the prime example.

Marathwada, a drought-prone region in Maharashtra, receives approximately 800 mm of annual rainfall – well below the state average. Despite this, sugarcane cultivation has expanded significantly there. Sugarcane consumes around 22.5 million litres of water per hectare during its 14-month growing cycle, compared to just 4 million litres over four months for chickpeas. Growing such a thirsty crop in a chronically water-stressed area is fundamentally at odds with the region’s hydrology.

As sugarcane farming has expanded, groundwater use in the region has surged. Maharashtra now pumps nearly three times more water for irrigation than India’s national average. This expansion has come at the direct expense of traditional crops. Farmers are increasingly abandoning crops like jowar (sorghum), bajra (pearl millet), and ragi (finger millet) – all of which are far less water-demanding and better adapted to the local climate.

Why do farmers choose sugarcane anyway?

Sugarcane is attractive because farmers can sell directly to sugar mills without middlemen taking a cut. The crop is also hardy – mature cane tolerates heavy rainfall or dry spells and is less vulnerable to pests than many alternatives. The sugar mill industry in Marathwada was initially promoted by politicians seeking to replicate the prosperity seen in other parts of Maharashtra, but it spread into areas where even drinking water is scarce.

A similar pattern exists in the Cauvery basin spanning Karnataka and Tamil Nadu, where sugarcane and paddy are cultivated in highly water-stressed regions. The Central Water Commission has flagged this mismatch between water-intensive cropping patterns and water availability as a critical national concern.

The crops these regions were traditionally known for – coarse cereals, millets, and pulses – are time-tested, drought-resistant, and nutritionally rich. Their displacement by commercial cash crops represents a double loss: ecological degradation and nutritional diversity decline.

Industrial development in ecologically sensitive areas

Poverty alleviation is often used to justify locating polluting industries, mining operations, and water-bottling plants in ecologically fragile zones. The logic seems reasonable on the surface: bring employment and economic activity to underdeveloped areas. But when these areas happen to be sensitive ecosystems – drylands, forests, coastal wetlands – the environmental cost can be devastating and often irreversible.

Unregulated and irresponsible mining activities in India have led to severe ecological damage, including deforestation, soil erosion, and loss of biodiversity. Large-scale mineral extraction without proper land restoration has resulted in widespread habitat destruction. Toxic chemicals and heavy metals released into water bodies affect aquatic ecosystems and pose serious health risks to communities that depend on these resources.

Mining and groundwater: a dangerous combination

Mining in fragile ecosystems is particularly problematic because of its impact on aquifer recharge. In drylands and semi-arid regions, the rate at which underground water replenishes depends on several factors: precipitation, underground flow patterns, evaporation rates, and the amount of soil and vegetation cover. When mining strips away vegetation and topsoil, it fundamentally disrupts the recharge process.

Coal mining – both surface and subsurface – causes enormous damage to flora, fauna, hydrological relations, and soil properties. Destruction of forests during mining operations is accompanied by extensive damage to the broader ecosystem. Heavy groundwater extraction by industrial units and bottling plants in these same areas adds further pressure on already depleted aquifers.

India has taken steps to address this. For instance, the government recently declared an Eco-Sensitive Zone around the Kumbhalgarh Wildlife Sanctuary in Rajasthan’s Aravalli range – one of the country’s most fragile ecosystems – which prohibits commercial mining, polluting industries, and brick kilns within the buffer zone. But such designations remain the exception rather than the rule, and weak regulatory action to limit groundwater demand continues to hinder progress, with only about 14% of overexploited blocks in the country currently notified for restrictions.

Groundwater depletion and cascading ecosystem damage

Underground water basins are renewable resources – but only if extraction does not exceed recharge. When it does, the consequences cascade through the entire ecosystem.

In drylands where vegetation has already been reduced by overgrazing, mining, or land conversion, both soil moisture and aquifer recharge rates decline together. Less vegetation means more surface runoff during rain (instead of infiltration), higher evaporation, and greater soil erosion. This accelerates a degradation spiral that is extremely difficult to reverse.

In Punjab, the situation is severe: if current depletion rates persist, groundwater levels could drop below 300 metres by 2039, potentially making the water unsuitable for both irrigation and domestic use. Close to 90% of India’s groundwater is used for crop irrigation, and the deepening water crisis is now a significant – though often overlooked – driver of rural-to-urban migration.

Saltwater intrusion in coastal areas

In coastal fragile ecosystems, over-extraction of groundwater creates a different but equally destructive problem: saltwater intrusion. When freshwater aquifers are drawn down below sea level, seawater seeps in to fill the void, contaminating the aquifer and often making it permanently unusable for drinking or irrigation.

As aquifers are depleted, reduced water discharge into coastal areas contributes to changes in salinity levels in estuarine and coastal waters. Mangrove ecosystems – vital for coastal biodiversity and natural storm protection – face direct threats from these altered salinity levels.

The destruction of an aquifer through over-extraction or saltwater contamination is not easily undone. Unlike surface water, which can recover within a season of good rainfall, aquifer restoration can take decades of sustained effort – if recovery is possible at all.

The case for resource valuation and conservation incentives

Sustainable resource use in fragile ecosystems is possible – but it requires that both local communities and government authorities recognise the ecological limits of a region and design policies accordingly. This starts with a fundamental shift: treating natural resources like groundwater, topsoil, and vegetation cover as assets with real economic value, not as free inputs for exploitation.

Proper pricing of natural resources

When groundwater is free and electricity to pump it is subsidised, there is no economic signal telling a farmer or an industry to conserve. Research shows that electricity subsidies substantially increase the common pool externality by encouraging investment in deeper wells that are socially wasteful – the costs of one farmer’s over-extraction are borne by all neighbouring users.

Proper pricing does not mean making water unaffordable for poor communities. It means structuring tariffs and subsidies so that basic needs are met affordably, while excessive commercial extraction faces real costs. The World Bank’s experience in India has shown that sustainable groundwater management ultimately depends on cross-sectoral reforms addressing the water-energy-agriculture nexus and providing the right incentives to resource users.

Community-based conservation approaches

Research evaluating World Bank interventions in India has found that mandatory regulatory policies alone – such as power regulation and credit restrictions – are not always effective in reducing groundwater depletion. Social regulation through participatory governance based on collective action can be more effective.

The Participatory Groundwater Management approach, implemented successfully in parts of peninsular India, empowers communities within a defined aquifer area by providing governance rights, awareness, and motivation for coordinated action. However, this approach has its limits – it does not work well where local institutions are weak or where droughts repeatedly undermine supply-side interventions.

Shifting cropping patterns to match ecology

Research published in Nature Communications demonstrates through optimisation modelling that India could meet its food procurement targets on average even without irrigation by shifting the geographies where crops are grown, while simultaneously increasing net farm income and arresting groundwater depletion. This is not a speculative idea – it is a data-driven finding that challenges the political status quo of concentrated procurement from a few water-stressed regions.

The key insight is that conservation after ecosystem disturbance is far more expensive and difficult than preventing disturbance in the first place. Once aquifers are contaminated, topsoil is eroded, or vegetation cover is destroyed, the investment required for restoration is orders of magnitude greater than what sustainable management would have cost.

Lessons for policy design in fragile ecosystems

The pattern across all these examples is consistent: policies designed in isolation – focused solely on economic output or poverty metrics – fail to account for ecological carrying capacity. The result is a short-term gain followed by long-term environmental and social loss.

Effective policy for fragile ecosystems needs to integrate several principles. First, subsidies must be aligned with sustainability limits – not blanket support for extraction but targeted assistance that rewards conservation. Second, cropping patterns should be guided by local agro-ecology, not by procurement politics or market incentives that ignore water availability. Third, industrial development in sensitive zones requires genuinely enforced environmental assessment – not rubber-stamped clearances driven by short-term economic targets.

Finally, local communities – who understand their ecosystems better than distant policymakers – must be genuine partners in governance. India’s indigenous peoples and local communities possess invaluable knowledge about sustainability and resilience, and they have a vital role in protecting fragile environments.

What do you think? Should governments be held accountable when their subsidy policies directly contribute to ecosystem collapse in fragile regions? And can market-based pricing of resources like groundwater ever be designed in a way that protects both the poorest communities and the environment?

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References
  1. https://www.nature.com/articles/s41467-022-31122-9
  2. https://thediplomat.com/2017/04/indias-thirsty-crops-are-draining-the-country-dry/
  3. https://yourstory.com/socialstory/2019/08/agriculture-india-water-scarcity

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Ecological Economics

1 The Ecology-Economy Interactions

  1. Introduction
  2. Evolution of Economic Thought and the Relationship with Ecology
  3. Modelling Environment-Economy Relationships

2 Energy Balance Principle

  1. Laws of Thermodynamics
  2. Characterization of Various Abiotic and Biotic Resources
  3. Absolute Scarcity and Sustainability
  4. Thermodynamics and Economic Analysis

3 The Ecological Limits to Economic Growth

  1. The Standard Model of Economic Growth
  2. The Ecological-Economic View of the Economy
  3. Human Biomass Appropriation, Climate Change, Ozone Shield Rupture
  4. Perspectives of the Ecological Limits
  5. Alternative Models of Production, Wealth and Utility

4 Development and Environment

  1. Economic Development and the Well being of the People
  2. Environment and Economic Growth
  3. Economic Development and Environmental Sustainability

5 Economic Theories of Renewable and Non-Renewable Resources

  1. Economics Theories of Renewable Resources
  2. Economics of Fishery: Bio-economic Model
  3. Regulation of Fishery
  4. Limitations of Steady-State Bio-economic Model
  5. Economic Theories of Non-renewable Resources
  6. Optimal Allocation of Non-renewable Resources
  7. Non-renewable Resources and Limits to Economic Growth

6 Resource Exploitation and Environmental Degradation

  1. Nature of Resources
  2. Natural Capital – Abiotic Resources
  3. Natural Capital –Biotic Resources
  4. Man-made Capital

7 Market, Trade and Environment

  1. Market, Functioning and Efficiency
  2. Market Failure, Externalities and Inefficiency
  3. Market Failure, and Public Goods and Inter-temporal Allocations
  4. Markets, Internationalization and Environment
  5. Market, Globalization and Environmental Degradation

8 Economic Activity- Impacts

  1. Co-evolutionary Economics
  2. Carrying Capacity, Population Dynamics and Extinction
  3. Carrying Capacity of the Human Population and the Ecological Footprint
  4. Concept of Overshoot and Dangers of Collapse
  5. Impact of Economic Activity on Climate Change
  6. Impact of Climate Change in the Context of India

9 Fragile Ecosystems, Livelihoods and Poverty

  1. Fragility of Ecosystems
  2. Poverty and Environmental Degradation in Fragile Ecosystems
  3. Bias Against Agriculture
  4. Poor and Natural Resource Based Livelihoods
  5. Private Rights, Public Property and Commercial Exploitation
  6. Shortsighted Government Policies
  7. The Fragile Himalayan Ecosystem
  8. Arid and Semi-arid Tracts in the Central and Western India
  9. Wetlands of India

10 Environmental Pollution Problems of India

  1. Environmental Pollution Problems of India
  2. Rural Air Pollution Problems
  3. Rural Water Pollution Problems
  4. Urban Noise Pollution
  5. Urban Water Pollution
  6. Urban Solid Waste

11 Common Pool Resources

  1. CPR’s in India
  2. CPR’s and Rural Areas of India
  3. Tragedy of Commons
  4. The Land based CPR’s in India: The Problems
  5. Poverty-Environment Linkages of CPR
  6. CPR’s, Traditional Knowledge and Community Conservation
  7. CPR Regime and Institutions

12 Gender and Environment

  1. Perspectives on Gender and Ecology
  2. Gendered Impacts of Environmental Degradation
  3. Women’s Environmental Activism
  4. Women and Natural Resource Conservation – An Assessment

13 Ecosystem Services and its Valuation

  1. Ecosystem Services and Its Valuation
  2. Methods and Techniques for Valuation of Ecosystem Services
  3. Steps in Ecosystem Service Valuation

14 Policy Instruments for Pollution Control, Conservation and Clean Energy

  1. Types of Environmental Policy Instruments
  2. Decentralized Policy Instruments
  3. Command and Control Regulations
  4. Market Based Instruments (MBI’s)
  5. Market Based Instruments and Developing Countries

15 Kyoto Protocol and Carbon Trading

  1. Climate Change and Need to Reduce Emissions
  2. Evolution of Kyoto Protocol
  3. The Kyoto Mechanisms
  4. Carbon Trading and Tradable Permits
  5. Kyoto Protocol and Impact Assessment

16 Green National Income Accounting

  1. Conventional GNP and Green GNP
  2. Integrated Environmental and Economic Accounting
  3. Flaws in the Conventional System of National Accounting
  4. Methodological Approaches to Green Accounting
  5. Green Accounting in India
  6. Issues and Challenges of Green Accounting
  7. Green Accounting and Sustainable Development