India’s natural resources – its forests, pastures, water bodies, and grazing lands – have long been shared by communities. But how these shared resources are managed is anything but simple. From tribal villages pooling private lands for collective farming to government-led forest conservation programmes, the institutions that govern common pool resources (CPRs) in India have taken many shapes over centuries. Understanding how these institutions emerge, evolve, and function is essential for anyone interested in sustainable development, rural livelihoods, or environmental policy.

Table of Contents

What are common pool resource institutions and why do they matter?

A common pool resource is any resource – like a forest, fishery, irrigation canal, or grazing land – that is costly to exclude people from using, but where one person’s use reduces what’s available for others. Think of a village pond: anyone nearby can draw water, but overuse leaves less for everyone. This creates the well-known challenge described as the “Tragedy of the Commons,” where shared resources get overexploited when nobody regulates their use.

A CPR institution is the set of rules, norms, and arrangements – formal or informal – that a community, government, or other body creates to manage such shared resources sustainably. These institutions define who can access the resource, how much they can extract, and what happens when someone breaks the rules.

Nobel laureate Elinor Ostrom demonstrated through extensive fieldwork across countries including India, Nepal, and Sri Lanka that communities can and do manage common resources effectively – challenging the assumption that only privatisation or government control can prevent resource degradation. Her research laid out design principles for robust CPR institutions, including clear boundaries, collective decision-making, and effective monitoring.

When does the common property regime become relevant?

Two fundamental questions drive the study of CPR management: when is a common property regime needed, and how does it come into being? CPR institutions tend to emerge under three main circumstances:

When private resource management fails: Individual ownership doesn’t always work, especially for resources that are diffuse or interconnected. If a single farmer cannot efficiently manage a large watershed or grazing area alone, collective management becomes necessary.

When there are scale advantages: Some resources – large irrigation systems, forests spanning several villages, river fisheries – are simply too big for one person or family to manage. Pooling effort and resources across a community allows for better maintenance, monitoring, and allocation.

When the state fails to manage public goods adequately: Government control of resources doesn’t always reach every village effectively. In many parts of India, centralised state management of forests, pastures, and water bodies has led to degradation rather than conservation. When this happens, communities often step in to fill the governance gap, developing their own rules and enforcement mechanisms.

Chakriya Vikas Pranali: a ground-up approach from Jharkhand

One of the most striking examples of a CPR institution built from the ground up is the Chakriya Vikas Pranali (CVP), or the Cyclic System of Development. Developed by soil conservationist P.R. Mishra, this model was first implemented in Sukhomajri, Haryana, and later extended to tribal areas in what is now Jharkhand (formerly part of Bihar).

The concept is straightforward but powerful: poor tribals and small farmers pool their private lands to create a commonly managed resource base. Everyone works, everyone protects, everyone contributes, and everyone receives a share of the combined output. The benefits from one cycle of investment become the capital for the next – hence the “cyclic” name.

The results were dramatic. In Sukhomajri, tree density increased from just 13 per hectare in 1976 to over 1,270 per hectare by 1992. Grass production rose from 40 kg per hectare to three tonnes per hectare in the same period. The village became prosperous enough that, by 1989, it was reportedly the first village in India to pay income tax.

The FAO has noted that the CVP model succeeded because it linked moisture conservation with economic activities that built social capital. Importantly, the programme is largely self-financed after initial investments, making it replicable – a quality many other CPR interventions lack.

Why is CVP significant for CPR theory?

CVP demonstrates that common property regimes can emerge even where resources were previously held privately. When individual management yields poor returns on degraded land, pooling resources collectively can unlock productivity gains impossible for any single farmer. This challenges the assumption that private property is always more efficient than collective management.

Three approaches to CPR institution development in India

CPR institutions in India have not evolved through a single path. Scholars have identified three distinct strands through which these institutions have developed:

1. Traditional management through conflict and learning

Long before formal policies existed, communities across India developed their own systems for managing shared resources. These traditional institutions are rooted in local social and cultural customs that have guided CPR use patterns – particularly in rural and tribal areas – for generations.

These systems did not emerge overnight. They evolved through repeated cycles of resource use, conflict, negotiation, and learning. Over time, communities arrived at workable rules governing who could harvest how much, when, and from where. Compliance was enforced through social pressure, cultural norms, and community sanctions rather than formal law.

Examples include the Bishnoi communities of Rajasthan, known for centuries of protecting Khejri trees and wildlife, the sacred grove traditions found across central India and the northeast, and the padu system in Kerala, where fishing communities use lottery-based rotational access to manage their catch equitably.

2. Customary laws introduced by governments

A second strand involves governments formally recognising or codifying customary practices into law. Rather than imposing entirely new systems, this approach takes existing community norms and gives them legal backing.

In India, this has a long history. The Indian Forest Act of 1927 included provisions for village forests, recognising the need for local control. More recently, constitutional protections under the Sixth Schedule for states like Nagaland and Mizoram have given legal standing to traditional tribal institutions that manage forests and common lands.

However, research on northeast India highlights a tension: customary governance systems increasingly operate within contested legal ground shaped by statutory law and development policies. The result is friction between the cultural legitimacy of community institutions and the state’s regulatory claims.

3. Responses to market or state failure

The third strand is reactive: CPR institutions emerge when existing management by the state or through market mechanisms breaks down. When government agencies fail to protect forests from encroachment, when irrigation systems fall into disrepair, or when unregulated market access leads to resource depletion, communities may organise collectively to address the gap.

This strand is particularly visible in India’s forest sector, where decades of centralised control during the colonial and post-independence periods failed to either conserve resources or support local livelihoods. Community frustration with top-down management created the conditions for newer participatory models to take root.

Traditional management systems: shifting cultivation in northeast India

Northeastern India offers a particularly rich example of traditional CPR management. Shifting cultivation, locally known as jhum, has been the dominant farming system across the region’s hilly tracts for centuries. It involves clearing a patch of forest, cultivating it for a season or two, and then abandoning it to allow natural regeneration while moving to a new plot.

This is not random or unregulated. Jhum is governed by detailed customary institutional rules that dictate the jhum cycle (how long land is left fallow), which families cultivate which plots, and how forest resources are shared during fallow periods. Village councils traditionally managed the allocation of jhum plots, enforcement of fallow periods, and dispute resolution.

In the 1950s, jhum cycles were typically maintained at around 30 years, which allowed adequate forest regeneration. However, population pressure and changing circumstances have shortened these cycles to as few as three to seven years in some areas by the late 1990s, undermining ecological sustainability.

The institutional framework around jhum also varies by tribe and region. In some communities, village land is communally owned but divided between clans. Customary law may allow families to convert jhum plots to permanent private holdings if they invest in improvements – a provision that, with the weakening of traditional authority, has sometimes led to elite capture of common lands.

Despite pressures to abandon it, jhum persists because it is deeply embedded in the cultural identity of tribal communities. It provides food security, maintains crop diversity (farmers grow up to 60 crops in mixed systems), and creates complex landscape mosaics that support biodiversity.

Modern institutional approaches: Joint Forest Management

The most prominent modern CPR institution in India is Joint Forest Management (JFM). It represents a direct response to the failure of centralised government forest management and is now one of the largest community-based natural resource management programmes in the world.

Origins of JFM

The story of JFM begins in the 1970s with the Arabari experiment in West Bengal. Ajit Kumar Banerjee, a forest officer, was struggling with constant disturbance from local villagers – grazing and illegal harvesting – in the Arabari Forest Range. Instead of cracking down, he negotiated an agreement with eleven surrounding villages: they would protect the forest, and in return, they would receive a share of the forest’s non-timber products and revenue.

The experiment was a success. Around the same time, a similar programme in Sukhomajri, Haryana, showed that community participation could dramatically improve forest cover while supporting local livelihoods. These early experiments convinced policymakers that top-down management alone was not working.

The 1988 National Forest Policy

The 1988 National Forest Policy marked a fundamental shift. Its primary aim was environmental stability and ecological balance, with economic extraction made secondary to conservation goals. Crucially, the policy recognised that forest conservation was not possible without active community participation.

The policy created formal space for communities to engage in forest management, and specifically acknowledged the rights of forest-dwelling communities regarding grazing lands and collection of non-timber forest products (NTFPs) such as fruits, medicinal plants, honey, and fodder. This was a significant departure from the earlier 1952 policy, which had prioritised national commercial interests over local needs.

In 1990, the Ministry of Environment and Forests issued guidelines formalising the JFM approach. Under these guidelines, village-level Forest Protection Committees (FPCs) enter into agreements with state forest departments. Villagers protect forests from fire, illegal grazing, and unauthorised harvesting; in return, they receive NTFPs and a share of timber revenue.

Scale and impact of JFM

JFM expanded rapidly. By the year 2000, 27 Indian states had adopted various JFM schemes, with over 63,000 Forest Protection Committees managing more than 140,000 square kilometres of forest land. The programme was further strengthened by a 2002 circular that provided legal status to JFM committees and mandated women’s involvement.

JFM is distinctive because it is neither purely top-down nor purely bottom-up – it is a structured partnership. This hybrid character is both its strength and its challenge. On the positive side, it brings government resources and legal authority together with local knowledge and daily presence. On the other hand, power imbalances between forest departments and village committees have sometimes undermined genuine community participation.

Challenges facing JFM

Research from the Economic and Political Weekly has pointed out that it is the underlying social structures – not just formally constituted bodies – that determine whether CPR management succeeds or fails. Local factions, power dynamics, and the specific history of each village shape outcomes as much as the formal rules do.

After three decades, some scholars have raised concerns about JFM losing its initial momentum. Questions remain about whether the model can sustain itself without continued external support, and whether the benefits truly reach the most marginalised forest-dependent communities.

The blend of traditional and modern: what works?

India’s experience shows that the most resilient CPR institutions tend to blend traditional and modern elements. The 1988 Forest Policy itself represents this – it draws on the long history of community forest management in India while providing a modern legal and administrative framework.

Successful institutions typically share certain characteristics: clearly defined resource boundaries, rules that match local conditions, mechanisms for collective decision-making, effective monitoring, graduated sanctions for violations, and accessible conflict resolution processes. These align closely with Ostrom’s design principles, developed from studying cases across the world including several from India.

The key insight from the Indian experience is that context matters enormously. A CPR institution that works in the forests of West Bengal may not work in the pastures of Rajasthan or the jhum lands of Nagaland. Facilitating agencies – whether government, NGOs, or external development organisations – must understand local dynamics, power structures, and resource characteristics before intervening.

The Cambridge Handbook of Commons Research emphasises that CPR development interventions in India are context-specific and typically go through iterative processes. External agencies do not simply act as catalysts – they actively influence decision-making through complex engagement with local communities.

Looking ahead: the future of CPR governance in India

India’s CPR institutions face new pressures today. Urbanisation is drawing people away from rural resource management. Climate change is altering the productivity and boundaries of shared resources. Market integration is creating incentives to privatise or overexploit common lands. And in many regions, traditional institutional authority continues to weaken as younger generations engage less with customary governance.

At the same time, there is growing recognition – both in policy and academia – that community-based resource management works when it is designed well and supported appropriately. The challenge is scaling successful models without losing the local specificity that makes them effective.

India’s diverse experience – from the cyclic development model in Jharkhand to jhum governance in the northeast to Joint Forest Management across the country – offers rich lessons for CPR governance anywhere in the world. The fundamental takeaway is that neither pure state control nor pure privatisation is a universal answer. Effective resource governance requires institutions that are adaptive, locally rooted, and equipped to balance ecological sustainability with livelihood needs.

What do you think? Can traditional community-based institutions for managing shared resources survive the pressures of urbanisation and market forces, or do they need to be fundamentally reinvented? And in your region, who do you think is best placed to manage common resources – communities, government, or some combination of both?

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References
  1. https://en.wikipedia.org/wiki/Common-pool_resource
  2. https://www.downtoearth.org.in/a-tribute-to–p-r-mishra-16317
  3. https://www.fao.org/4/a0270e/A0270E06.pdf
  4. https://www.sciencedirect.com/science/article/abs/pii/S0308597X03000873
  5. https://www.researchgate.net/publication/398528439_Common_Pool_Resources_in_North_East_India_Governance_and_Challenges
  6. https://onlinelibrary.wiley.com/doi/10.1111/ddi.13605
  7. https://www.fao.org/4/XII/0729-C1.htm
  8. https://link.springer.com/chapter/10.1007/978-94-017-9771-9_24
  9. https://subscription.epw.in/journal/2007/36/special-articles/institutionalising-common-pool-resources-management.html
  10. https://www.cambridge.org/core/books/abs/cambridge-handbook-of-commons-research-innovations/management-of-facilitated-common-pool-resources-in-india/44042C8EB0763E4E23CD84DE1D18DD27

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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