Case Study: Assistive Judicial Reasoning on Ecological Definitions

Aravalli case study showing how legal definitions can protect or expose ecology, and why constitutional determination of ecological dispensability must precede exposure to harm.

This case study shows why courts must decide whether terrain can be treated as ecologically dispensable before legal definitions necessarily expose it to foreseeable harm.

Ecological and institutional context

The Supreme Court of India has described the Aravalli Hills and Ranges (the Aravallis) as the indispensable ecological and socio-economic backbone of the region, functioning as the primary geographical barrier separating the arid north-western desert from the fertile northern plains. The Court has further characterised the Aravallis as the “green lungs” of north-western India, which have for centuries sustained diverse ecosystems and underpinned the livelihoods of numerous communities.[1]

Owing to their ancient geological formation, the Aravalli Hills and Ranges host some of the nation’s most significant mineral deposits. In this context, the Court has noted longstanding allegations of escalating anthropogenic pressures—including unchecked urbanization, systematic deforestation, and intensive resource extraction—exerting strain upon what it describes as an inherently fragile ecosystem.[1]

Definitional inconsistency and judicial engagement

In this context, the Supreme Court of India has been actively seized of issues concerning mining operations within the Aravallis since 1991, beginning with proceedings to enforce statutory protections over forest, wildlife, and ecologically sensitive areas. In that phase of the jurisprudence, the Court consistently held that where terrain was already legally protected, it could not be subjected to mining or other degrading activity, and that failures of enforcement could not be justified by administrative uncertainty.[2, 3, 4, 5, 6]

Related environmental jurisprudence also addresses the precautionary principle, ecological risk, and expert-assisted adjudication in upstream legal determinations.[7, 8, 9]

Committee records before the Court, including dissenting submissions, reflect long-running contestation over ecological protection in the Aravalli context.[10]

In its judgment dated 20 November 2025 in the present matter, the Court framed its concern as “the definition of Aravali Hills and Ranges and the need for the proper conservation of the same in the States of Delhi, Haryana, Gujarat and Rajasthan.”[11]

The Court accepted the findings of a Committee constituted for this purpose, including the definition of the Aravalli Hills and Ranges. As the Court subsequently recorded, “This definition served as the primary foundation for the Committee’s recommendation that ‘no new mining leases’ be granted within the newly demarcated ‘Aravalli Hills and Ranges’.”[1]

Judicial concern regarding definitional consequences

However, in its subsequent order of 29 December 2025, the Court expressly noted that definitional choices, if not carefully examined, may give rise to ambiguity and unintended consequences. The Court therefore observed that “there is a dire need to further probe and clarify to prevent any regulatory gaps that might undermine the ecological integrity of the Aravalli region.”[1]

Clarification prior to implementation

In the same order, the Court further observed that “prior to the implementation of the Committee’s Report, or the execution of the directions contained in paragraph 50 of this Court’s judgment dated 20.11.2025, a fair, impartial, independent expert opinion must be obtained and considered, after associating all requisite stakeholders.” The Court further emphasized that such a step is “essential to resolve critical ambiguities and to provide definitive guidance.”[1]

Purpose and scope of this simulation

This simulation is designed to assist that upstream exercise of clarification. It does not assess mining, projects, or specific sites. It is not an environmental impact assessment, and it does not depict a real map. Instead, it visualizes the legal and structural consequences that follow from adopting alternative definitional frameworks—the very issues the Court has identified as requiring clarification before downstream actions are taken.[1, 12] By showing how different definitions include or exclude terrain, the simulation makes visible how definitional choices can expose terrain to downstream processes of disturbance or disintegration. It does not determine whether such exposure is constitutionally permissible. Rather, it clarifies what is placed at risk of harm by definition, thereby underscoring the need to address the constitutional question of ecological dispensability of the terrain under Articles 21 and 48A, read with the precautionary principle, intergenerational equity, and the doctrine of public trust.[13, 14, 15]

Do Definitions Legally Protect Ecology?

Nothing on this terrain changes as you scroll.

The hills do not move.

The valleys do not shift.

Only the definition changes — and with it, what is treated as protected and what is excluded.

This is not a map of any real place.

It is a visual aid for noticing something subtle but powerful:

how definitional choices alone can determine what becomes legally exposed before any activity begins.

Please use a desktop device to see how a map of synthetic terrain visually displays the impact of the questions below.

Q1 — Do definitions equally protect and unprotect ecology?
You will see the same terrain six times. Nothing physical changes. Only the definition does. Watch how each definition produces a different protection outcome — without altering a single hill or valley.
Choice D1 — Mountains are defined by local relief ≥ 100 m[16]
  • Protection concentrates on the highest landforms.
  • Lower terrain is excluded by definition.
Choice D2 — Ranges are defined by aggregation of nearby hills (≤ 500 m)[16]
  • Protection expands to include the space between hills.
  • Proximity is treated as unity.
Choice D3 — Mountains are defined by enclosing slopes (> 3° with buffers)[17]
  • Protection forms pockets around steep areas.
  • Gentle slopes and valley floors may remain outside.
Choice D4 — Mountains are defined as composite terrain systems (elevation + slope + relief)[18]
  • Protection begins to follow connected structure rather than a single threshold.
Choice D5 — Mountains are defined by functional ecological corridors[19]
  • Protection follows continuity and connection.
  • Isolated peaks matter less than ecological flow.
Choice D6 — Mountains are defined by watershed units and upstream-downstream linkages[20]
  • Protection extends across connected drainage terrain, including upstream areas shaping downstream water flow and quality.
Observe: A definition is a legal act, not a neutral label. Once a boundary is chosen, some terrain is treated as legally protected and some is placed outside legal protection.
Q2 — What causality does the legal act of definition unlock?
Hold one definition steady. First see full ecological capability. Then see the capability that lies outside protection under the same definition. This is the causal moment: exclusion by definition renders capability legally exposable.
Terrain with capability to support forests
  • Some forest-capable terrain lies outside protection under the same definition.
Terrain with capability to regulate or serve as watershed
  • Water-regulating capability often extends into valleys and gentle slopes beyond protected boundaries.
Terrain with capability to sustain ecological corridors
  • Connectivity can be excluded even while individual peaks remain protected.
Terrain with capability to function as wind and climate barriers
  • Climate-regulating capability can fall outside protection when definitions track form, not function.
Observe: No project has begun and no harm is yet visible. But legal exposure has already been created upstream by definition.
Q3 — Does mapping ensure ecological protection?
This map now highlights only excluded ecological capability under the selected definition. It shows where exclusion creates legal exposure before downstream approvals are considered.
Excluded capability: Forest-supporting terrain
  • What is highlighted here is not “degraded.” It is excluded — and therefore exposable.
Excluded capability: Watershed-regulating terrain
  • The boundary follows the definition, not the water.
Excluded capability: Corridor continuity
  • A system can be fragmented by exclusion while individual hills remain protected.
Excluded capability: Climate-regulating terrain
  • Climate function can disappear from protection when mapping tracks shape, not role.
Observe: Mapping can show what is excluded. It cannot decide whether that excluded ecology is constitutionally dispensable.
Q4 — Was exposure created without prior constitutional determination of ecological dispensability?
Q2 showed full ecological capability. Q3 showed capability rendered legally exposable by definitional exclusion. No step determined ecological dispensability before exposure to harm. This sequencing makes the inversion visible: exposure occurs first, and determination of dispensability is missing.
Exposure before dispensability: Forest-supporting capability
  • This capability is exposed by exclusion before any determination is made whether exposing it to harm can occur without loss of ecological function, identity, and continuity.
Exposure before dispensability: Watershed-regulating capability
  • Exposure happens first; determination of ecological dispensability comes later.
Exposure before dispensability: Ecological corridor capability
  • Connectivity can be exposed to disintegration before any determination is made whether that exposure is ecologically dispensable.
Exposure before dispensability: Climate-regulating capability
  • Climate-regulating capability can be exposed to disintegration without prior determination that it is ecologically dispensable.
Observe: Constitutional determination must precede exposure. If exposure comes first, the non-delegable constitutional sequence is reversed.
What This Means for Ecological Integrity
A boundary is not only a line. It is a legal condition. Once terrain is excluded by definition, it becomes legally exposable to downstream processes before any downstream action begins.
Downstream processes

Downstream processes are the ordinary mechanisms through which legally exposed terrain may be acted upon: land-use change, extraction, fragmentation, hydrological alteration, infrastructure insertion, and cumulative disturbance. These processes do not begin with projects or permissions; they begin when exposure is created by definition.

Whether such processes may be permitted turns on their effect on ecological integrity.

Ecological integrity

Ecological integrity is the emergent result of the continuity of relationships among parts of an ecosystem that allow it to function as a whole. When those relationships are broken, no amount of replacing, upgrading, or compensating individual parts can restore the system’s function, identity, or continuity.

Ecological dispensability

Ecological dispensability is the ability to expose a part of an ecosystem to harm without losing the function, identity, and continuity it gives to the whole.

That determination must precede exposure being treated as permissible and cannot be deferred to downstream assessment.[13, 14, 15]

Environmental impact assessment
  • Operates after exposure is treated as permissible.
  • Evaluates consequences and mitigation, not whether exposure itself should have been allowed.
  • By the time assessment begins, the definitional decision that created exposure has already been made.[12]
Observe: If exposure begins with definition, then deciding what may be exposed cannot be left to downstream processes. This simulation does not determine what must be protected. It makes visible why the constitutional determination of ecological dispensability must come first— and why that determination cannot be avoided.

What Then Is the Unanswered Question?

Across legal systems, a common distinction exists.

Some decisions are about managing impact — how to reduce harm, how to mitigate damage, how to regulate use.

Other decisions come earlier. They concern whether certain terrain or ecological capability should be exposed to harm at all.

That earlier question is not scientific in nature. Science can explain what ecological functions exist and how harm occurs. It cannot decide whether those functions may be sacrificed.

Nor is it an administrative or executive question. Regulation, planning, and impact assessment operate only after exposure is treated as permissible in principle. They manage consequences; they do not decide foundational limits.

In constitutional systems, that foundational limit is set by instruments that protect the conditions of life, continuity, and obligation across generations.

International recognition of the right to a clean, healthy, and sustainable environment affirms the legal importance of protecting ecological conditions essential to life and well-being.[21]

In India, this role is performed by the Constitution itself — through the right to life under Article 21, the duty to protect the environment under Article 48A, and the principles that flow from them, including precaution, public trust, and intergenerational equity.[13, 14, 15]

These principles point to a simple but unavoidable requirement: before terrain is exposed to degradation by definition or exclusion, it must first be determined whether it is ecologically dispensable.

Once exposure is permitted, assessment and regulation can follow. But they cannot decide what should never have been exposed in the first place.

That unanswered question — of ecological dispensability — belongs to this earlier, constitutional category.

Interactive exploration

Choose and combine definitions, combine logic, and toggle capabilities to see how exposure changes.

Definition sources: D1-D2 [16], D3 [17], D4 [18], D5 [19], D6 [20].

REFERENCES
  1. In re: Definition of Aravalli Hills and Ranges and ancillary issues, Suo Motu W.P. (C) No. 10 of 2025 (Sup. Ct. India Dec. 29, 2025) (Order).
  2. Ministry of Environment & Forests, Notification S.O. 319(E), Gazette of India, 7 May 1992, available via eGazette portal. Search by notification number: S.O. 319(E); date: 07-05-1992.
  3. Tarun Bharat Sangh, Alwar v. Union of India & Ors., (1993) Supp. (3) S.C.C. 115 (India).
  4. Tarun Bharat Sangh, Alwar v. Union of India & Ors., W.P. (C) No. 509 of 1991 (Sup. Ct. India Oct. 11, 1991) (Order).
  5. Tarun Bharat Sangh, Alwar v. Union of India & Ors., W.P. (C) No. 509 of 1991 (Sup. Ct. India Nov. 26, 1991) (Clarificatory Order).
  6. Tarun Bharat Sangh, Alwar v. Union of India & Ors., W.P. (C) No. 509 of 1991 (Sup. Ct. India May 14, 1992) (Record of Proceedings and Order).
  7. A.P. Pollution Control Board v. Prof. M.V. Nayudu, (1999) 2 S.C.C. 718 (India).
  8. T.N. Godavarman Thirumulpad v. Union of India & Ors., (1997) 2 S.C.C. 267 (India) (forest-conservation continuing mandamus in W.P. (C) No. 202 of 1995).
  9. K.M. Chinnappa & T.N. Godavarman Thirumulpad v. Union of India & Ors., (2002) 10 S.C.C. 606 (India).
  10. Anil Agarwal, Dissenting Report submitted to the Supreme Court Committee (Nov. 2, 1992) (W.P. (C) No. 509 of 1991).
  11. In re: Issue relating to definition of Aravalli Hills and Ranges, W.P. (C) No. 202 of 1995 (Sup. Ct. India Nov. 20, 2025) (Judgment and Directions).
  12. United Nations Environment Programme, Environmental Impact Assessment Training Resource Manual, 2d ed. (2002).
  13. Constitution of India, arts. 21, 48A.
  14. M.C. Mehta v. Kamal Nath, (1997) 1 S.C.C. 388 (India).
  15. Vellore Citizens’ Welfare Forum v. Union of India, (1996) 5 S.C.C. 647 (India).
  16. Press Information Bureau, Govt. of India, Aravalli definition criteria release (Dec. 21, 2025).
  17. Forest Survey of India, India State of Forest Report 2023, Vol. 2.
  18. Kapos, V., Rhind, J., Edwards, M., Price, M. F., & Ravilious, C., UNEP-WCMC, Mountains of the World (2000).
  19. Hilty, J. et al., Guidelines for conserving connectivity through ecological networks and corridors (IUCN, 2020).
  20. FAO, Watershed management, SFM Toolbox module.
  21. G.A. Res. 76/300, The human right to a clean, healthy and sustainable environment, U.N. Doc. A/RES/76/300 (July 28, 2022).
How to cite this case study

Bluebook: Systems Innovators, Case Study: Assistive Judicial Reasoning on Ecological Definitions, Systems Innovators (Feb. 14, 2026), https://systems-innovators.com/pages/resources/case-study-assistive-judicial-reasoning-on-ecological-definitions/.

APA: Systems Innovators. (2026). Case study: Assistive judicial reasoning on ecological definitions. Systems Innovators. https://systems-innovators.com/pages/resources/case-study-assistive-judicial-reasoning-on-ecological-definitions/

Synthetic terrain, fixed grid: 10 km × 10 km (100 km²) · Resolution: 100 m (1 ha) per cell
Elevation
Low (~200 m) High (~900 m)
The lines you draw shape causality