The current landscape of environmental law in India is defined by a growing contradiction between large-scale afforestation policies and the lived realities of forest communities. Since the 2023 amendment to the Forest Conservation Act, the government has accelerated the creation of land banks to facilitate compensatory planting. While these initiatives are framed as climate mitigation strategies, they often overlook the ecological distinction between complex, old-growth ecosystems and the high-density monoculture plantations that frequently replace them.
In regions like Bankura, West Bengal, the implementation of these schemes has led to direct legal friction with the Forest Rights Act of 2006. Many indigenous groups find their ancestral grazing lands and community forests enclosed for state-led ‘Green Credit’ projects, often without the mandatory consent of the Gram Sabha. This shift has effectively commodified the environment, prioritising the accumulation of ‘Net Present Value’ and carbon credits over the constitutional and socio-economic rights of the people who have managed these landscapes for generations.
As of 2026, the judiciary is increasingly tasked with reconciling these ind environmental goals with the protection of biodiversity and human rights. Recent rulings from the Supreme Court and the National Green Tribunal highlight a widening gap between official forest cover statistics and the actual health of forest ecosystems. This article examines the ‘ghost forests’, areas that are legally classified as forest but lack biological function, and argues that the current jurisprudential approach fails to address the systemic displacement of tribal populations in the name of conservation.
In the 2026 legal landscape, ‘ghost forests’ are defined as land tracts that are officially recorded as ‘forest cover’ in government databases but lack the biological complexity, biodiversity, and ecosystem services of natural forests. This term specifically targets failed compensatory afforestation projects where high mortality rates leave behind standing dead wood or barren plots that exist only as legal placeholders for diverted primary forests. These sites often result from ‘quick fix’ planting strategies designed to meet statistical targets rather than ecological restoration goals.
Legally, these areas represent a breakdown in the ‘Net Present Value’ (NPV) system, in which the financial compensation paid for forest diversion fails to support a living ecosystem. In 2026, the focus has shifted toward the ‘monoculture trap’, where state-sponsored plantations of non-native species like Eucalyptus or Acacia create ‘green deserts’.
The Ecological Failure of Monocultures
Monoculture plantations, frequently utilised in compensatory afforestation to replace diverted primary forests, represent a significant ecological failure due to their lack of structural and functional diversity. Unlike natural forests, which consist of multi-layered canopies and a variety of species, monocultures are uniform stands of a single species, usually chosen for rapid growth. This uniformity makes the entire plantation highly susceptible to specialised pests and diseases, as there are no ‘barrier’ species to slow the spread of an outbreak, often leading to total stand collapse.
From a hydrological perspective, monocultures of non-native species like Eucalyptus or certain pine varieties often deplete local water tables. These species are frequently selected for their high biomass production, which requires significant water consumption compared to indigenous, slow-growing hardwood species. This creates a ‘drying effect’ on the surrounding soil, negatively impacting local agriculture and reducing the moisture available for undergrowth, which eventually turns the forest floor into a biological desert.
The failure of monocultures also extends to their inability to support local fauna and soil health. Natural forests provide a complex web of food sources and nesting sites that monocultures cannot replicate; without diverse leaf litter, the soil microbiome suffers, leading to nutrient depletion and erosion over time. Furthermore, the carbon sequestration potential is often overestimated, as they lack the deep soil carbon storage capacity found in the undisturbed root systems and fungal networks of ancient, primary forests.
The Legal Fiction of ‘Green Cover’
The legal fiction of ‘green cover’ arises from the administrative reliance on canopy density as a proxy for ecosystem health, a metric that treats all tree-covered land as ecologically equivalent. Under current Indian forestry standards, any area over one hectare with a canopy density of more than 10% is classified as ‘forest’, regardless of whether it is a thriving ancient ecosystem, a commercial timber plantation, or an orchard. This classification allows the state to claim stable or increasing forest cover in official reports even as high-biodiversity primary forests are diverted for mining or infrastructure projects.
This statistical inflation creates a ‘paper forest’ effect where the loss of complex habitat is masked by the planting of saplings in distant land banks. Legally, this satisfies the requirements of the Compensatory Afforestation Fund Act (CAMPA), but it ignores the ‘time lag’ and ‘functional loss’ inherent in forest destruction. A primary forest takes centuries to develop its soil profiles and symbiotic fungal networks, yet the law allows for its immediate replacement by a numerical equivalent of saplings that may not survive past the first three years.
Furthermore, the 2023 Forest Conservation Act has intensified this fiction by narrowing the legal definition of what land requires protection. By excluding ‘deemed forests’, lands that were not formally notified but fit the textbook definition of a forest, from the ambit of the law, the government can facilitate the clearance of natural groves while maintaining the ‘green cover’ narrative through monoculture plantations elsewhere. This legal decoupling of ‘greenery’ from ‘ecology’ serves to commodify the landscape, turning forests into replaceable assets on a balance sheet rather than protected biological entities.
The legislative framework governing forest conservation in India has undergone a radical transformation, shifting from a protectionist stance to a more compensatory and market-oriented model. Central to this regime are the Compensatory Afforestation Fund Act (CAMPA) and the Forest Conservation (Amendment) Act of 2023, which together create the legal pathway for diverting natural forests in exchange for monetary payments and the establishment of new plantations. This framework operates on the principle of ' Net Present Value’, attempting to quantify the economic worth of an ecosystem to justify its destruction, while simultaneously redefining ‘forest land’ to streamline industrial clearances.
Compensatory Afforestation Fund Act (CAMPA)
The Compensatory Afforestation Fund Act (CAMPA) serves as the financial backbone of India's forest diversion policy, managing thousands of crores in funds collected from industries that clear forest land. These funds are intended to be utilised for ‘compensatory afforestation’ and the maintenance of new plantations to offset the environmental damage caused by industrial projects. However, the mechanism has faced significant criticism because it centralises financial control, often bypassing the local communities who are directly impacted by the loss of the original forest.
A primary legal and administrative challenge within CAMPA is the ‘Net Present Value’ (NPV) collection, which attempts to put a price on the ecological services lost when a forest is felled.
In the 2024-2026 period, the focus has intensified on the massive unspent balances within the state and central funds, which frequently lead to rushed, top-down planting drives that ignore local ecological suitability. These funds are often used to establish plantations on common lands or ‘revenue forests’, leading to territorial conflicts with tribal populations who rely on those lands for their livelihood.
Furthermore, the CAMPA framework has been critiqued for institutionalising the ‘replacement’ logic, where the payment of money is seen as a legal discharge of the responsibility to protect the environment. This has led to a ‘pay-and-pollute’ culture where the ecological integrity of ancient forests is traded for the promise of future plantations that may never reach maturity. In 2026, judicial audits of CAMPA spending have increasingly highlighted that while the fund is growing, the actual survival rate of the forests it finances remains alarmingly low and poorly documented.
In Odisha's Kalahandi and Kandhamal districts, CAMPA projects have triggered intense local resistance, notably in villages like Gundurupi and Burlubaru. Conflict erupted when the Forest Department fenced off lands already granted to tribal communities under the Forest Rights Act (FRA).
By planting commercial teak without Gram Sabha consent, the state restricted access to traditional food and non-timber forest produce. Communities protested this ‘land grab’, viewing these fenced-off plantations as encroachments on ancestral titles.
Forest Conservation Act of 2023
The Forest Conservation (Amendment) Act of 2023, now officially renamed the ‘Van (Sanskaran Evam Samvardhan) Adhiniyam’ represents a fundamental shift in how India legally identifies and protects forest land. The most significant change is the narrowing of the Act's scope to apply only to lands officially notified as ‘forest’ under the Indian Forest Act (1927) or recorded in government records after October 25,1980. This effectively removes the legal protections previously granted to ‘deemed forests’, vast tracts of land that ecologically function as forests but are not formally registered, thereby facilitating their conversion for industrial use without the rigorous oversight once required.
A major point of legal and environmental contention is the ‘100 km exemption rule’, which allows for the diversion of forest land within 100 kilometres of India's international borders for strategic national security projects without seeking prior central clearance. In 2026, critics highlight that this blanket exemption covers almost the entirety of ecologically sensitive Northeastern states and the Himalayan belt, areas rich in endemic biodiversity.
The Act now also explicitly reclassifies activities like silvicultural operations, safaris and eco-tourism as ‘forestry activities’, allowing them to be established within protected areas without being treated as ‘non-forest’ diversions.
The 2023 Amendment also significantly impacts the rights of indigenous communities by diluting the mandatory requirement for Gram Sabha consent, a cornerstone of the Forest Rights Act (FRA) of 2006. By streamlining the ‘Fast Track’ clearance process, the Act makes it easier for the state to allocate forest land for compensatory afforestation ‘land banks’ or private plantations without the prior informed consent of the tribal dwellers who live there.
The legislative pivot has moved India's forest policy away from a community-based conservation model toward a centralised, market-linked approach that treats forest land as a tradable commodity for carbon offsetting and industrial expansion.
The creation of ‘land banks’ for compensatory afforestation has emerged as a primary driver of tribal displacement in 2026. By earmarking community commons and ancestral grazing lands for future plantations, the state effectively encloses vital resources, stripping forest-dwelling tribes of their traditional livelihoods and legal protections without physical relocation.
The ‘Land Bank’ Phenomenon
The ‘land bank’ phenomenon in 2026 refers to the systematic practice of state governments identifying and setting aside vast tracts of ‘degraded’ or ‘waste’ lands to be used for future compensatory afforestation. These banks serve as a ready inventory to satisfy the legal requirements of the Forest Conservation Act whenever a project proponent diverts natural forest land elsewhere. By pre-authorising these areas for plantations, the state streamlines the industrial clearance process, treating land as a modular asset.
However, this administrative convenience frequently masks a deep-seated human rights crisis. In many instances, the lands designated for these banks are not ‘waste’ but are the ancestral commons, grazing grounds, and community forests of indigenous tribes. Once a plot enters a land bank, it is often fenced off or placed under forest department control, effectively enclosing the commons. This leads to ‘non-physical displacement’, where communities are stripped of their livelihoods and traditional access to forest produce without being technically evicted from their homes, bypassing the resettlement protections usually triggered by physical displacement.
Case Study: Bankura District
In the town I reside in, Bankura, situated in West Bengal, the creation of land banks has become a focal point of resistance for Santhal and Munda communities. Large swathes of land, locally classified as ‘jungle mahals’, have been earmarked for compensatory afforestation to offset industrial mining and infrastructure projects in other districts. This administrative reclassification often ignores the existing ‘Community Forest Resource’ (CFR) claims made under the Forest Rights Act. By fencing off these areas for monoculture plantations, the Forest Department has restricted tribal access to non-timber forest produce (NTFP) like ‘Sal’ leaves and ‘Mahua’ flowers, which are critical to the local socio-economic fabric.
The Bankura case highlights a ‘double displacement’: tribes lose their ancestral forests to industry and then lose their alternative grazing lands to the ‘green’ compensation for that industry. In 2026, reports hinted at increasing skirmishes between local Gram Sabhas and forest officials over the plantation of commercial species that do not support local biodiversity. These projects are more often than not initiated without the ‘prior informed consent’ of the villagers, showcasing a direct implementation gap between constitutional safeguards and ground-level forestry practices.
The legal conflict between the Forest Rights Act (FRA) 2006 and compensatory schemes centres on the erosion of tribal sovereignty. While the FRA mandates Gram Sabha consent for any land diversion, compensatory projects often bypass this, reclassifying community commons as state land banks, thereby undermining the statutory rights of forest-dwelling communities.
The Supremacy of the Gram Sabha
The Forest Rights Act (FRA) of 2006 establishes the Gram Sabha as the supreme authority in forest governance, mandating its ‘prior informed consent’ for any land diversion. This statutory power is designed to prevent the historical injustice of state-led displacement.
However, by 2026, this supremacy is under siege. Executive rules frequently bypass these assemblies to expedite ‘Green Credit’ projects or land bank formations.
Focusing on the ‘Green Credit Project’ once again, I want to elaborate on it. A ‘Green Credit Project’ is a market-based incentive scheme launched by the Indian government to encourage voluntary environmental actions by individuals, communities, and private industries. Unlike traditional carbon markets that focus solely on carbon dioxide emissions, the ‘Green Credit Program’ (GCP) assigns a ‘tradeable value’ to various environmental activities, such as water conservation, waste management, and most controversially, large-scale tree planting. The primary mechanism involves entities undertaking eco-friendly projects on degraded land or within community commons to earn ‘Green Credits’. These credits can then be sold on a domestic exchange to corporations or individuals who wish to meet their environmental, social, and governance (ESG) targets or offset their ecological footprint.
When a Gram Sabha's veto is ignored or falsified, it constitutes a direct violation of constitutional protections, rendering the subsequent compensatory afforestation legally tenuous and socially exploitative.
Circumvention Tactics
Circumvention tactics in 2026 involve a sophisticated blend of administrative reclassification and the strategic ‘splitting’ of projects to evade environmental oversight. One method is the fraudulent documentation of Gram Sabha consent, where attendance sheets from unrelated social welfare meetings are repurposed as ‘No Objection Certificates’ for forest diversion. Additionally, state authorities often utilise ‘Fast Track’ portals to approve land bank transfers before local communities can formally register their claims under the Forest Rights Act, effectively presenting the clearance as a ‘fait accompli’.
In the 2024-2026 judicial term, the Supreme Court of India and the National Green Tribunal (NGT) have shifted focus toward the quality and survival of compensatory forests. Landmark proceedings in the ‘T.N. Godavarman case’ now demand that states provide standardised, georeferenced data to verify ‘deemed forests’ and plantation health.
The NGT has increasingly issued ‘survival audits’, rejecting the mere payment of Net Present Value (NPV) as a fulfilment of environmental duty. These rulings reinforce the principle that financial compensation cannot replace ecological function, prioritising the constitutional right to a healthy environment over administrative statistical claims.
In case anyone is unaware, the ‘T.N. Godavarman Thirumulpad v. Union of India’ (1996) is the most significant environmental litigation in Indian history, often referred to as the ‘Forest Case’. Originally filed to stop illegal timber felling in the Nilgiris, it evolved into a ‘continuing mandamus’ where the Supreme Court effectively took over the management of India's forests. The landmark aspect of the 1996 interim order was the expansion of the definition of ‘forest’ beyond government records to include any land that satisfies the ‘dictionary meaning’ of a forest, regardless of ownership. This case is named after T.N. Godavarman Thirumulpad, a member of the Nilambur Royal Family in Kerala. Godavarman filed the original petition (Writ Petition No. 202 of 1995) out of a personal and environmental concern regarding the ‘unregulated felling of timber’ and the destruction of the pristine Gudalur forests in Tamil Nadu.
Valuation of Nature (Net Present Value)
Net Present Value (NPV) is a mandatory financial levy paid by project proponents to compensate for the ‘loss of ecosystem services’ when diverting forest land. In 2026, the Supreme Court refined this valuation to include non-market benefits like carbon sequestration, soil conservation, and water purification. Critics nonetheless argue that this ‘economic valuation’ reduces complex living systems to a balance sheet. By assigning a price to biodiversity, the law inadvertently legitimises the destruction of irreplaceable ancient forests, provided the ‘correct price’ is paid into the CAMPA fund, creating a transactional relationship with nature that ignores its intrinsic worth.
The NGT's Stance on Survival Rates
By 2026, the National Green Tribunal (NGT) has mandated ‘Survival Audits’ for all compensatory afforestation projects, rejecting the practice of self-reporting by forest departments. The Tribunal has ruled that if survival rates fall below 70-80%, project proponents must fund fresh plantations and face penalties. This jurisprudence challenges the ‘green cover’ fiction, asserting that ecological restoration is not complete until a self-sustaining ecosystem is established, thereby holding authorities accountable for the thousands of crores spent via CAMPA funds.
This section focuses on the qualitative failure of replaced landscapes. Critics argue that state-led afforestation projects prioritise statistical ‘greenery’ over biological integrity, failing to replicate the complex carbon storage, hydrological cycles, and diverse habitats found in the primary forests they ostensibly replace.
Primary Forests vs. Plantations
Primary forests are irreplaceable, self-sustaining ecosystems featuring complex vertical structures, ancient carbon-rich soils, and diverse endemic species.
In contrast, compensatory plantations in 2026 are frequently monocultures of fast-growing species like Eucalyptus or Teak. These ‘green deserts’ lack the ecological depth to support local fauna or provide the same hydrological benefits as natural stands. Research indicates that plantations capture significantly less carbon over long cycles and are more vulnerable to diseases and wildfires. The legal substitution of primary forests with plantations ignores this ‘functional loss’, trading a vibrant, multi-layered biological heritage for a uniform, low-biodiversity timber crop.
Carbon Sequestration Capacity
Primary forests function as massive, stable carbon repositories, storing significantly more carbon in their undisturbed soils and ancient biomass than young plantations. In 2026, FAO (Food and Agriculture Organisation of the United Nations) data confirms that while India ranks 5th globally in carbon sequestration, absorbing 150 Mt CO2 annually, this capacity is increasingly threatened by the replacement of high-integrity forests with plantations. Young monocultures sequester carbon faster during initial growth but lack the deep soil carbon stocks and long-term storage stability of primary ecosystems. Consequently, replacing a mature forest with a plantation results in a ‘carbon debt’ that takes decades, or even centuries, to repay.
The ‘Time Lag’ Problem
The ‘time lag' issue represents a fundamental temporal disconnect in India's compensatory afforestation policy. While the destruction of a primary forest occurs instantaneously, the ‘replacement’ forest requires decades, if not centuries, to replicate the lost ecological functions. During this transition period, which often spans 30 to 50 years, there is a total collapse of ecosystem services, including local climate regulation, water table recharge, and habitat connectivity. This creates an ‘interim loss’ that is rarely accounted for in financial valuations like the Net Present Value (NPV).
By 2026, scientific audits have highlighted that many plantations fail before they ever reach maturity due to poor maintenance or ecological unsuitability. This means the carbon debt incurred by felling ancient trees is never actually repaid. The legal fiction that a future sapling is an immediate substitute for a centuries-old tree ignores the reality that biodiversity and carbon sequestration are time-dependent processes that cannot be accelerated by administrative mandates.
Sounds commercialised, right? Well, the commodification is indeed commercial in nature. It refers to the transformation of complex ecosystems into standardised, tradable assets.
In the current year, this shift is driven by policies like the Green Credit Program and the Net Present Value system, which assign monetary figures to biodiversity and carbon sequestration. By reducing forests to ‘carbon units’ or ‘biodiversity offsets’, the law treats environmental degradation as a solvable accounting problem. This market-driven approach ignores the intrinsic, non-monetary value of nature, facilitating a ‘pay-to-pollute’ culture where finance is mistakenly viewed as an equal substitute for irreplaceable biological heritage and indigenous spiritual connections to the land.
The ‘Green Credit Program’ (GCP)
The Green Credit Program (GCP), notified under the Environment (Protection) Act, represents a paradigm shift toward market-based environmentalism in India. Unlike traditional carbon markets, the GCP creates a tradeable ‘Green Credit’ for a broad spectrum of ecological activities, including water conservation, sustainable agriculture, and waste management. However, its most significant and debated component is ‘compensatory afforestation’. Under this framework, public or private entities can proactively plant trees on ‘degraded’ land to earn credits. These credits can then be sold to corporations or developers to offset their ecological footprint or satisfy regulatory mandates for forest clearance. By 2026, the government will have streamlined the ‘Green Credit Portal’ to facilitate seamless trading, aiming to incentivise private sector participation in restoration. The program is positioned as a tool to mobilise finance for climate action, effectively turning environmental stewardship into a competitive commodity that can be bought and sold on a national exchange.
Despite its innovative structure, the GCP faces intense scrutiny regarding its impact on society and ecology. Critics argue that the program facilitates ‘greenwashing’ by allowing companies to purchase a clean conscience without reducing their actual emissions or the destruction of primary forests. A major concern in the identification of land, many areas labelled as ‘degraded’ or ‘wastelands’ are originally vital community commons or grazing lands used by pastoralists and tribal groups. By 2026, reports indicate that Green Credit projects often bypass the ‘prior informed consent’ of Gram Sabhas, leading to the enclosing of lands that are central to rural livelihoods. Alongside, the focus on rapid sapling plantation to generate credits often results in low-biodiversity monocultures that fail to provide the complex ecosystem services of natural forests. This commodification risks prioritising market liquidity over long-term ecological health, potentially creating ‘paper forests’ that fail to support local communities or wildlife.
Socio-Economic Erasure
Socio-economic erasure in the context of afforestation refers to the systematic ‘rendering invisible’ of human lives, cultures, and economies that depend on lands labelled as ‘degraded’ or ‘wastelands’. When the state identifies land for its land banks or Green Credit projects, it often employs a purely cartographic logic that ignores the lived reality of the landscape. For the Santhal, Munda, and other forest-dwelling communities, the forest is a multi-generational pharmacy, a supermarket and a spiritual sanctuary. By fencing off these areas for monoculture plantations, the state effectively erases the informal economies built around non-timber forest produce (NTFP).
The erasure is facilitated through three primary mechanisms:
Ultimately, socio-economic erasure serves the ‘Green Credit’ logic by clearing the human ‘clutter’ from the balance sheet. It allows nature to be managed as a sterile, corporate asset, while the people who have protected these landscapes for centuries are relegated to the status of encroachers on their own ancestral soil.
The jurisprudential critique of India's compensatory afforestation framework centres on the fundamental tension between State Sovereignty and Constitutional Rights. At its core, the current legal regime operates on the principle of ‘eminent domain’, where the state's power to seize land for the ‘greater good’ frequently overrides the statutory protections granted to forest-dwelling communities. In 2026, legal scholars identify a widening gap between the Forest Rights Act (FRA) 2006, which recognises historical rights, and the Forest Conservation (Amendment) Act 2023, which streamlines land diversion.
The primary gap lies in the procedural dilution of consent. While the Supreme Court has historically upheld the Gram Sabha's authority, executive rules have increasingly shifted the burden of proof onto the marginalised. Jurisprudentially, this represents a move from ‘Substantive Justice’, where the ecological and social health of the forest is protected, to ‘Formalistic Justice’, where environmental compliance is satisfied by a mere financial transaction into the CAMPA fund. This ‘market logic’ creates a legal vacuum where the intrinsic value of nature and the lived rights of indigenous peoples are replaced by tradeable credits and fiscal penalties, effectively decoupling environmental law from social equity and ecological reality.
Constitutional Failures
The constitutional failure of compensatory afforestation lies in the systematic erosion of Article 21 (Right to Life) and the ‘Fifth and Sixth Schedules’, which protect tribal autonomy. By 2026, the administrative push for land banks has created a direct conflict with the ‘Dignity of Life’ guaranteed to forest-dwellers. When the state forcibly encloses community commons for plantations, it uproots the socio-economic foundation of marginalised citizens, violating their right to a livelihood.
Furthermore, the ‘doctrine of public trust’, which mandates that the state hold natural resources in trust for the people, has been replaced by a ‘doctrine of fiscal trade-off’. Under this shift, the executive treats constitutional safeguards like the Gram Sabha's veto (upheld in the Niyamgiri judgement) as mere procedural hurdles rather than mandatory democratic checkpoints. This bypass of decentralised governance represents a failure of Article 48A, as the state ‘protects the environment’ through top-down monocultures while simultaneously destroying the democratic fabric of the very landscapes it claims to save. Ultimately, the law has prioritised a balance sheet over the ‘Socialist’ and ‘Democratic’ promises of the Preamble, turning citizens into subjects of an economic bureaucracy.
The implementation gap in India's forest policy represents the chasm between ambitious legislative intent and the ground reality of ecological decay. By 2026, this gap is defined by ‘administrative inertia’, ‘technical manipulation’, and a ‘culture of compliance’ that prioritises paperwork over physical survival. While the CAMPA fund has accumulated over ₹50,000 crores, the translation of these funds into self-sustaining ecosystems remains negligible.
One primary driver of this gap is the ‘geographic mismatch’ between where forests are lost and where they are ‘replaced’. Forest land is frequently diverted in ecologically sensitive zones like the Western Ghats or the Himalayas, while compensatory afforestation is carried out in distant, semi-arid regions of different states. This results in a localised ecological collapse that cannot be ‘compensated’ by saplings planted a thousand kilometres away. Furthermore, the reliance on satellite-based monitoring provides a distorted picture of success. Remote sensing often classifies invasive species, commercial orchards, and monoculture plantations as ‘forest cover’, hiding the loss of primary biodiversity under a cloak of green pixels.
The ‘Survival Rate Crisis’ further illustrates this failure. In 2026, field audits by the NGT revealed that in several states, the reported 90% survival rate was actually closer to 30% on the ground due to poor site selection, lack of irrigation, and grazing pressures. The ‘implementation’ ends at the planting stage; there is no institutional mechanism for the long-term ‘care’ of these forests.
Finally, the ‘Governance Gap’ persists because the forest bureaucracy remains insulated from community oversight. By bypassing the Gram Sabhas and ignoring traditional ecological knowledge, the state implements top-down models that fail to survive because they lack local ‘ownership’. The result is a cycle of ‘paper forests’ where budgets are spent, records are cleared, but the landscape remains ecologically barren.
The future of India's environmental jurisprudence hinges on reconciling economic growth with ecological and social integrity. By 2026, it has become clear that the current model of compensatory afforestation is suffering from a ‘credibility crisis’. While the Supreme Court and NGT have introduced more rigorous survival audits and refined valuations like NPV, these remain technical fixes for a systematic problem. The persistent ‘time lag’ and the qualitative difference between a primary forest and a plantation cannot be solved by financial transactions alone.
To move forward, the legal framework must shift from a ‘commodification’ mindset to one of ‘ecological restoration’. This requires:
Ultimately, the law must recognise that nature is not a replaceable asset on a ledger. True ‘compensation’ for the loss of an ancient forest is impossible. Therefore, the judicial focus must shift toward ‘absolute conservation’ and a rights-based approach that protects both the forest and the communities that serve as its natural guardians.
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