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Enregistrement W7163986783 · doi:10.5281/zenodo.20612812

Waste Management Practices in Indian Urban Construction Sites: Challenges and Opportunities

2016· article· en· W7163986783 sur OpenAlexaff
Premalatha T G

Notice bibliographique

RevueOpen MIND · 2016
Typearticle
Langueen
DomaineEngineering
ThématiqueRecycled Aggregate Concrete Performance
Établissements canadiensImpact
Organismes subventionnairesnon disponible
Mots-clésDemolitionSustainabilityDemolition wasteUrbanizationIncentivePopulationEnforcementSustainable development

Résumé

récupéré en direct d'OpenAlex

Abstract The rapid urbanization of India has driven a massive surge in infrastructure development, resulting in a dramatic increase in Construction and Demolition Waste (CDW). The introduction of the Construction and Demolition Waste Management Rules, 2016 marked a critical turning point, mandating systematic collection, segregation, and processing. However, a decade after its introduction, the sector faces significant hurdles in implementation. This article provides an in-depth analysis of the post-2016 landscape, identifying the widening gap between policy intent and ground-level execution. It explores the persistence of linear "take-make-dispose" models, the challenges in market acceptance of recycled aggregates, and the emerging opportunities for a circular construction economy. By examining technical, socio-economic, and regulatory facets, the study concludes that achieving true sustainability requires robust institutional enforcement, technical capacity building, and market-driven incentives to transform waste into a secondary resource. Keywords: CDW, India, 2016 Rules, Circular Economy, Sustainable Construction, Environmental Engineering, Civil Infrastructure 1. Introduction The Indian construction sector serves as a vital engine for economic growth, contributing significantly to national GDP and providing essential employment opportunities. Yet, this rapid development is simultaneously a major contributor to resource depletion and environmental degradation. With the urban population projected to exceed 50% by 2030, the demand for residential, commercial, and transportation infrastructure has reached an unprecedented high. Consequently, the generation of CDW—estimated to range between 150 and 530 million tonnes annually—has emerged as a pressing urban crisis that threatens the structural and environmental viability of Indian cities. Before the 2016 notification of the Construction and Demolition Waste Management Rules, construction debris was largely viewed as an "invisible" waste stream, often handled through informal, unregulated channels or illegal dumping in sensitive ecosystems, riverbeds, and peripheral urban lands. The 2016 Rules fundamentally shifted this dialogue, mandating a formal, systematic approach to the life cycle of construction materials. However, the sheer scale of urban construction activity continues to outpace the development of necessary waste processing infrastructure. As cities expand vertically and horizontally, they grapple with the ecological consequences of unmanaged debris, including the loss of productive land to illegal landfills and the degradation of groundwater quality. This article adopts a civil engineering lens to evaluate how we must transition from passive disposal to active material recovery through systematic technological and administrative intervention. The shift is not merely administrative; it is an engineering necessity to preserve the finite natural resources required for India’s future infrastructure. Furthermore, as the scarcity of high-quality river sand and virgin stone aggregates becomes more pronounced, recycled alternatives are evolving from a "green" luxury into an economic and structural necessity for the modern Indian engineer. We are transitioning from a landscape where rubble is a burden to one where it is an essential raw material for sustainable urban densification. The objective of this review is to map the current state of CDW management and provide a rigorous framework for stakeholders—from urban planners to private contractors—to operationalize circular economy principles, essentially viewing the city as an "urban mine." 2. The 2016 Regulatory Landscape: Intent vs. Reality The 2016 Rules were designed to bring clarity and accountability to the complex construction value chain. Key provisions included: Mandatory Segregation: Generators are legally required to keep C&D waste unmixed at the point of origin. This is intended to facilitate the recovery of high-value materials like steel, aluminum, and copper wiring, which are often lost when waste is commingled with inert materials like concrete and bricks. Proper segregation at the source is the single most important variable in achieving high-purity recycled output. Without this upstream control, downstream processing plants face contamination issues that degrade the final product quality. Infrastructure Requirements: Municipal authorities in cities with populations exceeding one million are strictly mandated to commission and operate C&D waste processing facilities. This decentralized model aims to reduce the carbon footprint associated with long-distance waste transport, which typically accounts for 20-30% of total waste management costs. Mandatory Procurement: A crucial policy lever was the requirement for government infrastructure projects to utilize 10–20% of recycled C&D products, such as aggregates, concrete blocks, and manufactured sand, to stimulate the secondary materials market. Despite these clear mandates, implementation remains highly fragmented. While major metropolitan hubs like Delhi and Ahmedabad have successfully commissioned large-scale recycling plants, many mid-sized cities struggle with basic collection systems. The lack of standardized operating procedures (SOPs) often results in processed materials failing to meet the rigorous quality benchmarks required by structural engineers, thereby undermining the market demand for recycled goods. Furthermore, the absence of stringent "Polluter Pays" enforcement mechanisms means that dumping remains a cheaper, albeit illegal, alternative for many contractors who prioritize short-term profit over environmental accountability. Without standardized testing protocols for Recycled Concrete Aggregates (RCA), engineers are often reluctant to specify these materials in critical load-bearing applications. The policy must evolve from mere mandates to proactive technical verification systems that validate the structural safety of recycled materials. Only through the establishment of accredited certification labs can we overcome the current reliance on "rule-of-thumb" material selection and move toward performance-based specifications that explicitly account for recycled content without compromising safety factors. This institutional gap underscores the need for a national CDW certification board that provides transparent data on the material properties of recycled inputs, allowing engineers to confidently specify recycled materials in designs, knowing they comply with IS (Indian Standard) codes. 3. Engineering and Environmental Challenges Effective management is hindered by several persistent, deep-seated barriers: Hydrogeological Impact and Leaching: From an environmental engineering standpoint, the dumping of CDW into low-lying areas or wetlands is a significant chemical threat. Construction debris often contains hazardous components—such as trace amounts of heavy metals from paints, asbestos, or industrial adhesives—which, when subjected to rain-induced percolation, lead to the leaching of contaminants into subsurface soil and aquifers. This alters the soil’s pH levels and porosity, creating a legacy of contamination that persists long after the construction site is closed. Engineering studies have shown that leaching from CDW dumpsites increases the concentration of sulfates, chlorides, and heavy metals in nearby groundwater, necessitating long-term remediation efforts that are often more costly than the original disposal should have been. This degradation of local aquifers poses a direct health risk to urban populations relying on groundwater, and it requires engineers to implement advanced site-capping, liner systems, and leachate-collection systems that are currently absent in most regional landfill planning. Enforcement Gaps and Digital Monitoring: Urban Local Bodies (ULBs) often lack the technical personnel and digital monitoring systems necessary to track waste flow from the point of generation to final disposal. Without real-time data, it is difficult to penalize illegal dumping or verify that contractors are utilizing authorized facilities. Effective enforcement requires the integration of GIS-based tracking and the deployment of municipal waste auditors who can certify that contractors have adhered to site-specific Waste Management Plans. The lack of transparency in the logistics chain allows for widespread "leakage" into the informal dumping market, which hides the true cost of construction on the environment. We must move toward blockchain-enabled manifests that track the weight and composition of debris from the building demolition site directly to the processing plant, ensuring verifiable cradle-to-gate accountability. Market Quality Perception and Engineering Standards: RCA often face skepticism from the engineering community. Architects and civil engineers, accustomed to the consistency and high strength of virgin materials, remain skeptical about the long-term structural integrity of recycled alternatives. This skepticism is exacerbated by a lack of awareness regarding current processing technologies—such as optical sorting and mobile crushing—that can now produce high-quality aggregates meeting national standards. The mechanical properties of RCA, particularly water absorption and bond strength, can be optimized through modern processing. However, the lack of widespread certification programs remains a barrier to adoption. We need a robust national testing framework that categorizes RCA based on strength, allowing for safe usage in non-structural and semi-structural applications. Increased investment in pilot-scale demonstration projects that prove the structural reliability of RCA is a prerequisite for wider market adoption and for the development of code-compliant design tables. Informal Sector Integration: The collection and disposal ecosystem remains dominated by unorganized, informal actors. Wh

Récupéré en direct depuis OpenAlex et désinversé. Les résumés ne sont pas conservés dans cette base de données : les index inversés représentent 8,6 Go des 9,3 Go de texte de la base, et le serveur dispose de 13 Go libres.

Comment cette classification a été obtenuedéplier

Prédiction distillée sur la base complète

Imitation des enseignants

Ni prévalence calibrée, ni vérité terrain. Validation humaine à venir. Apprise à partir de 10 348 étiquettes directes de Codex et de 10 348 étiquettes directes de Gemma. Le mode candidate est l'union des têtes enseignantes seuillées; le consensus est leur intersection. Ces sorties portent le statut machine_predicted_unvalidated et ne sont ni des étiquettes humaines ni des étiquettes directes de modèles de pointe.

score de la tête « metaresearch » (Codex)0,000
score de la tête « metaresearch » (Gemma)0,000
Version: codex-gemma-dda1882f352aStatut de validation: machine_predicted_unvalidated
Catégories candidatesaucune
Catégories consensuellesaucune
DomaineSignal candidat: aucune · Signal consensuel: aucune
Devis d'étudeSignal candidat: Autre devis · Signal consensuel: aucune
GenreSignal candidat: Empirique · Signal consensuel: Empirique
Score de désaccord entre enseignants0,996
Score d'incertitude au seuil0,427

Scores Codex et Gemma par catégorie

CatégorieCodexGemma
Métarecherche0,0000,000
Méta-épidémiologie (sens strict)0,0000,000
Méta-épidémiologie (sens large)0,0000,000
Bibliométrie0,0000,000
Études des sciences et des technologies0,0000,000
Communication savante0,0000,001
Science ouverte0,0000,000
Intégrité de la recherche0,0000,000
Charge utile insuffisante (le modèle a refusé de juger)0,0000,000

Scores machine (provisoires)

Les deux têtes enseignantes du modèle étudiant, lues sur ce travail. Un score ordonne la base pour la relecture; il n'affirme jamais une catégorie, et le statut de validation accompagne chaque rangée tel quel.

Scores de référence d'un modèle non mature (critères de maturité non atteints, 7 itérations). Un score ordonne; il n'affirme jamais une catégorie.

Tête enseignante Opus0,089
Tête enseignante GPT0,274
Écart entre enseignants0,185 · la distance entre les deux têtes enseignantes sur ce seul travail
Statut de validationscore_only:v0-immature-baseline · tel quel depuis la passe de notation : score_only signifie que le nombre peut ordonner les travaux, et qu'aucune étiquette de catégorie n'en découle

Classification

machine, non validée

Prédiction automatique; un appel candidat d’une seule tête enseignante, pas un consensus.

Les modèles n’ont appliqué aucune catégorie : rien dans la taxonomie ne correspondait à ce travail.
Devis d'étudeAutre devis
Domainenon disponible
GenreEmpirique

Le détail, modèle par modèle et score par score, se trouve en fin de page sous « Comment cette classification a été obtenue ».

En bref

Citations0
Publié2016
Routes d'admission1
Résumé présentoui

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