By Green Architects — The Grove · The Landscape Consortium, Tiruchirappalli, Tamil Nadu

A cement plant is one of the most demanding environments in which to establish living vegetation — alkaline dust, water scarcity, compacted and rocky substrata, heavy vehicle movement and relentless heat all work against the very green belt that regulation and good practice require. This article sets out, from first principles and current evidence, why industrial green belts around cement works so often struggle, and how a landscape-architecture-led approach turns a compliance obligation into a durable, biodiverse and genuinely protective landscape.

Executive Summary

Green belt development is a legal condition of operation for every cement plant in India and a central pillar of the industry’s environmental, social and governance (ESG) commitments. Environmental clearance conditions typically require that a green belt be developed across roughly one-third of the plant area, planted at high density with native species and maintained to a defined survival rate (MoEFCC, 2006; CPCB, 1999). Yet a large proportion of industrial plantations underperform — not because trees will not grow near cement plants, but because the green belt is treated as a planting event rather than as an engineered, decade-long landscape system.

The technical difficulty is real and specific. Continuous deposition of alkaline cement dust raises soil pH, encrusts foliage and suppresses photosynthesis (Lamare & Singh, 2020); process and fugitive dust originate from crushers, raw and cement mills, kilns, clinker coolers, packing plants, conveyor corridors, raw-material yards and the limestone quarry itself (Nguyen et al., 2021; CPCB, 1999). Water is scarce and often saline or recycled; substrates are compacted, rocky or composed of mine overburden; and the operating environment subjects young plants to heat, wind, mechanical damage and the constant churn of expansion. Each of these is individually manageable, but together they explain why survival rates fall short and why belts thin out within a few years of the ceremonial first planting.

This article approaches the problem as a landscape architect and horticulturist would. It reviews the regulatory basis (CPCB green-belt guidelines, the EIA Notification 2006, National Ambient Air Quality Standards, and the 2025 rationalisation of green-cover norms by pollution potential); it quantifies what a well-designed belt actually delivers in dust interception, gaseous uptake, noise attenuation, carbon sequestration and microclimate control; and it translates that into design, species selection, soil rehabilitation, irrigation, maintenance and monitoring protocols suited to South Indian cement sites, with particular reference to the Ariyalur cement belt of Tamil Nadu. It closes with documented case studies — led by The Ramco Cements’ 800-acre Eco Park at Pandalgudi and UltraTech’s mine-boundary planting at Reddipalayam — a catalogue of the twenty-five most common failure modes, a project manager’s checklist, ten reference tables and six recommended figures. The consistent message is that the difference between a failed plantation and a thriving green belt is not the budget for saplings; it is the quality of site diagnosis, species matching, soil and water engineering, and multi-year aftercare.

Introduction

Why green belts matter in the cement sector

The cement industry occupies an unusual position in industrial ecology. It is simultaneously essential to national development — cement is the second most consumed material on earth after water — and one of the most emissions-intensive manufacturing processes, responsible for approximately seven to eight per cent of global anthropogenic carbon dioxide emissions (IEA, 2018; World Economic Forum, 2024). A cement works is also a concentrated, highly visible source of particulate matter, and it is usually paired with a limestone quarry that extends its environmental footprint across hundreds of hectares. Against this backdrop, the green belt is the single most cost-effective, publicly legible and ecologically productive mitigation measure available to a plant. It is a living air filter, a carbon sink, a noise and visual buffer, a habitat and a statement of environmental intent, all at once.

Industrial ecology treats a factory not as an isolated machine but as an organism embedded in a landscape, exchanging materials and energy with its surroundings. A green belt is the clearest expression of this idea in practice: it re-integrates the plant into the local ecosystem, intercepting pollutants at the boundary, moderating the microclimate, harvesting rainwater, stabilising disturbed soils and providing refuge for pollinators, birds and small fauna displaced by industrial land use. Where the belt is designed as an ecological system rather than a decorative screen, it begins to deliver measurable ecosystem services that compound year on year as the canopy matures.

Pollution mitigation, compliance and sustainable industrial landscapes

From a pollution-control standpoint, vegetation works through well-understood mechanisms. Leaves intercept and retain airborne particulates on their surfaces; stomata absorb gaseous pollutants such as sulphur dioxide, oxides of nitrogen and ozone; canopies deflect, refract and absorb sound; and transpiration and shade cool the air and surfaces around the plant (CPCB, 1999; US EPA, n.d.). A dense, multi-tiered belt of the right species, placed correctly relative to the emission sources and prevailing wind, converts a proportion of the plant’s fugitive emissions into trapped, settled or metabolised material before they reach the site boundary and the surrounding community.

From a compliance standpoint, the green belt is not optional. It is written into the environmental clearance (EC) that every cement plant must obtain before construction, and its progress is reported to regulators through the Environmental Management Plan and half-yearly compliance statements (MoEFCC, 2006). Increasingly it is also a material ESG disclosure: large Indian producers report tree numbers, green-cover area, biodiversity baselines and mine-rehabilitation progress in their sustainability and Business Responsibility and Sustainability Reports, and international operators benchmark biodiversity across their entire quarry portfolios (Ambuja Cements, 2025; Holcim, n.d.).

The ambition of this article is to bridge the gap between the regulatory requirement and the ecological reality. A green belt that merely satisfies a percentage-of-area rule but fails to survive, or that survives as a sparse monoculture with little filtering capacity, serves neither the plant nor the community. A green belt engineered as a sustainable industrial landscape — diverse, resilient, correctly irrigated and properly maintained — protects air quality, supports biodiversity, sequesters carbon, improves worker wellbeing and strengthens the plant’s social licence to operate. Achieving the second outcome rather than the first is a technical discipline, and that discipline is the subject of what follows.

Cement Industry Overview: Understanding the Environment the Green Belt Must Survive

Designing a green belt without understanding the plant that generates its stresses is like prescribing medicine without a diagnosis. A cement works is a sequence of crushing, grinding, pyroprocessing and packing operations, each of which loads the surrounding landscape with dust, gases, noise or heat. The green belt must be engineered to survive and to counteract these specific loads, which means the landscape architect must read the plant as a series of source zones.

Dust generation and emission points

Particulate matter is released at every comminution and thermal stage of the process. Limestone and raw-material crushers, raw mills, the rotary kiln, clinker coolers, cement (finish) mills and packing plants are the discrete point sources, each typically fitted with electrostatic precipitators or bag filters to control stack emissions (Nguyen et al., 2021). Even with modern arrestment, the sheer scale of material handled means that leakage, upset conditions and bypass events periodically increase local deposition. India’s stack particulate standards for cement plants are stringent, but ambient conditions at the boundary are governed by the National Ambient Air Quality Standards, which set the annual limit for PM₁₀ at 60 µg/m³ and for PM_2.5 at 40 µg/m³ (CPCB, 2009).

Fugitive dust — the green belt’s primary target

The emissions a green belt is best placed to intercept are not the tall, filtered stack plumes but the low-level fugitive dust generated across the site: from open limestone and raw-material storage yards, conveyor transfer corridors, unpaved haul roads, vehicle movement and the exposed quarry face. This dust is coarse, settles quickly and concentrates near the ground — exactly the height band that a well-structured, multi-tier planting can filter. Indian regulators explicitly frame green belts as pollution “sinks” for this fugitive load (CPCB, 1999). The design consequence is important: the densest, roughest-leaved, most dust-tolerant species belong on the rows facing the crusher, the yard and the haul road, not distributed evenly around a decorative perimeter.

Gaseous emissions and carbon

Cement is among the most carbon-intensive materials produced at scale. The International Energy Agency’s roadmap attributes roughly seven per cent of global carbon dioxide emissions to cement, at an intensity of about 0.54 tonnes of CO₂ per tonne of cement, of which sixty to seventy per cent is process emission from the calcination of limestone and the remainder is fuel combustion (IEA, 2018). Because most of the carbon is chemically unavoidable, offsetting and sequestration measures — including on-site afforestation — carry particular weight in the sector’s decarbonisation narrative. The kiln also generates oxides of nitrogen and, depending on fuel and raw-meal sulphur, sulphur dioxide; vegetation contributes modestly to removing these gases through stomatal uptake (CPCB, 1999).

Noise

Comminution equipment is loud. In-plant measurements at cement works record limestone crushers at around 97 dB(A), crusher hoppers above 100 dB(A), and raw mills, cement mills, coal mills and the rotary kiln in the 88–91 dB(A) range — with compressor rooms exceeding 103 dB(A) — against an occupational limit of 85 dB(A) over eight hours (Nguyen et al., 2021). While a vegetation belt cannot substitute for engineering controls at source, a dense belt more than about 30 metres deep provides a meaningful additional 4–8 dB(A) of attenuation at the boundary, together with valuable visual and psychological screening (see Species Selection and Design sections).

Heat island and microclimate

Large, paved, low-vegetation industrial sites behave like localised heat islands. Paved and built surfaces in comparable settings can run several degrees warmer than vegetated surroundings, and dark surfaces can reach temperatures far above air temperature on hot days (US EPA, n.d.). This elevated heat load stresses both workers and young plants, and it is precisely what a maturing canopy moderates through shade and transpiration — a virtuous circle in which the green belt improves the conditions for its own survival.

Mining and quarry influence

The limestone quarry that feeds the plant is an environmental unit in its own right. Overburden removal, drilling, blasting, loading and haul-road traffic degrade land and generate both suspended and deposited dust, and the resulting spoil and overburden create some of the most difficult substrates for planting anywhere in the industrial landscape. Progressive rehabilitation of mined-out areas — terracing, re-soiling, dense native planting and re-grassing — is now a core expectation of mine-closure planning and a major arena for green-belt and afforestation work at Indian cement operations (UltraTech Cement, 2025).

The Ariyalur context

Nowhere in Tamil Nadu is this more concentrated than in Ariyalur district, officially styled the “Land of Cements,” where the district administration records seven cement plants and dozens of major-mineral limestone leases in a compact belt (Ariyalur District Administration, n.d.). For a Tamil Nadu landscape practice, the Ariyalur–Perambalur belt, together with the older India Cements works at Sankarnagar in Tirunelveli and the Ramco operations in Virudhunagar, defines the real-world canvas on which industrial green-belt design must perform: hot, semi-arid, alkaline-dust-laden and water-constrained.

Regulatory Framework

Green-belt development in India sits at the intersection of pollution-control guidance, environmental-clearance conditions and, increasingly, corporate ESG disclosure. Understanding the framework matters because it defines the minimum obligations a plant must meet — and because good design consistently exceeds those minimums for sound ecological reasons.

CPCB green-belt guidelines

The foundational technical document is the Central Pollution Control Board’s Guidelines for Developing Greenbelts (PROBES/75/1999–2000), issued under the Ministry of Environment and Forests (CPCB, 1999). Rather than prescribing a single fixed tree count, the guideline is built around a dispersion-and-attenuation logic: it treats the belt as a pollutant sink whose effectiveness depends on width, height, foliage density and distance from the source, and it supplies extensive species lists organised by bio-climatic zone, favouring pollution-tolerant native species with high foliage surface area. It is the intellectual basis for the “select the right species, in the right structure, in the right place” approach that underpins all credible green-belt design. State pollution control boards issue parallel guidance in the same tradition (Bihar SPCB, n.d.).

MoEFCC environmental clearance and the EIA Notification 2006

The binding legal instrument is the Environmental Impact Assessment Notification, 2006, under which cement plants appear as Schedule item 3(b) (MoEFCC, 2006). Integrated plants at or above one million tonnes per annum are appraised centrally as Category A projects; smaller units and stand-alone grinding units are appraised by the State authority as Category B. Green-belt development is a standard condition of the clearance. In a representative recent clearance for a cement expansion, the condition required a three-tier green belt across at least 33 per cent of the total project area, planted with native species along the periphery at a tree density of not less than 2,500 per hectare — in that instance amounting to roughly 16 hectares of green belt and some forty thousand saplings (Shree Digvijay Cement, 2023). These figures are typical of the sector: green belt over about one-third of the site, high planting density, native species and a specified survival rate, commonly around 80 per cent (Rajasekaran et al., 2019).

The Environmental Management Plan

The green belt is budgeted, scheduled and monitored within the plant’s Environmental Management Plan (EMP), a mandatory component of the EC process. The EMP ties the belt to a capital and recurring budget, links it to air, water, noise and soil monitoring, and commits the plant to annual survival assessment and gap-filling of dead saplings. Compliance is reported to the regulator half-yearly, increasingly with photographic and geotagged evidence and, under recent norms, drone imagery (UltraTech Cement, 2025).

The 2025 rationalisation of green-cover norms

In October 2025 the MoEFCC moved from a uniform 33 per cent rule toward green-cover requirements graded by a project’s pollution potential, with the most polluting (“red”) air-emitting sectors held to a defined tier and lighter categories to lower percentages, supported by half-yearly drone-based reporting (ESG Broadcast, 2025). Cement, as a highly polluting sector, sits in the upper tier. Two practical points follow. First, plants already operating under a 33 per cent EC condition generally remain bound by that condition. Second, the direction of travel is toward verified green cover — measured, monitored and evidenced — rather than nominal area, which rewards belts that actually establish and survive. (The exact graded percentages should be confirmed against the original MoEFCC Office Memorandum before being quoted in a compliance document.)

Ambient air quality standards

The green belt ultimately serves the National Ambient Air Quality Standards, 2009, which set annual and 24-hour limits for particulate matter and gases at the plant boundary and in surrounding settlements: PM₁₀ at 60 (annual) and 100 (24-hour) µg/m³; PM_2.5 at 40 and 60 µg/m³; with corresponding limits for SO₂ and NO₂ (CPCB, 2009). A belt’s real success is measured not by the number of trees planted but by its contribution to keeping boundary concentrations within these limits.

ISO 14001, ESG and enforcement

Beyond statutory compliance, green belts feature in voluntary and market frameworks. An ISO 14001 environmental management system embeds the belt within a plan-do-check-act cycle of objectives and monitoring, and ESG and Business Responsibility and Sustainability Reporting increasingly quantify tree numbers, green cover and biodiversity outcomes for investors (Ambuja Cements, 2025). The consequences of neglect are equally real: the National Green Tribunal continues to hear enforcement matters concerning cement-plant dust control and green-belt adequacy, underlining that green-belt obligations are actively policed rather than nominal (Down To Earth, 2026). In Tamil Nadu, the State Pollution Control Board administers consent conditions and monitors green-belt compliance at each plant.

Objectives of Industrial Green Belts

A well-conceived green belt is asked to do many things at once. Setting these objectives out explicitly at the design stage is what allows them to be prioritised, measured and — critically — reconciled where they conflict. The following are the functions a cement-plant green belt is expected to deliver.

Dust filtration

Interception of fugitive particulate matter is the primary rationale for the belt. Foliage captures dust on leaf surfaces, where it is retained until washed off by rain or removed at leaf-fall. Capture efficiency varies enormously by species and leaf structure: guideline data for Indian species record dust-holding capacities of the order of 4–5 g per square metre of leaf surface for high performers such as teak and mango (Bihar SPCB, n.d.), and species studies in Tamil Nadu and elsewhere confirm that rough, hairy, large and densely arranged leaves trap the most particulate (see Plant Selection). A belt of the right species can substantially reduce the ground-level dust load reaching the boundary.

Carbon sequestration

Every tree in the belt is a small, permanent carbon store, and the belt as a whole is a modest but genuine offset against the plant’s process emissions. Sequestration rates are species- and site-dependent; fast-growing Indian species can fix several tonnes of carbon per hectare per year, while a conservative planning figure for a young tropical tree is of the order of 22 kg of CO₂ per tree per year (Kaul et al., 2011; Tree-Nation, n.d.). Over a mature belt of tens of thousands of trees, this accumulates into a reportable and ESG-relevant carbon benefit.

Biodiversity enhancement

A diverse, multi-layered belt provides food and shelter for pollinators, birds and small fauna, re-establishing a functioning micro-ecosystem on an otherwise sterile industrial site. Native fruiting and flowering species, understorey shrubs and undisturbed ground layers turn the belt from a green screen into living habitat — a shift that international operators now measure formally through biodiversity indicator systems (Holcim, n.d.).

Noise attenuation

A dense belt deeper than roughly 20–30 metres, with a continuous multi-tier structure and no gaps, deflects, refracts and absorbs sound, contributing an additional few decibels of attenuation over the effect of distance alone, and — just as importantly — removing the visible source, which reduces perceived noise (academic guidance summarised in the Species section). Its value is greatest where housing or sensitive receptors lie close to crushers or mills.

Wind velocity reduction and shelter

Structured as a shelterbelt or windbreak, the belt reduces wind speed to leeward, suppressing the pick-up and transport of loose dust from yards and haul roads and reducing evaporative stress on both plants and workers. Wind reduction is a design outcome of belt height, density and orientation relative to the prevailing wind.

Visual screening

The belt screens the industrial mass of the plant from roads, settlements and approach routes, softening the visual impact and signalling environmental stewardship. Visual screening is often the objective most valued by the surrounding community and by plant management, and it is achieved by tall, dense, evergreen species on the sightlines that matter.

Microclimate improvement and worker wellbeing

Shade and transpiration lower air and surface temperatures within and downwind of the belt, improving conditions for workers and reducing the heat-island effect discussed above. Access to green space and shaded amenity areas is associated with improved wellbeing, and progressive plants increasingly design parts of the belt as usable green amenity for staff.

Ecological restoration

Finally, on mined-out land and disturbed ground, the belt becomes the vehicle for ecological restoration — rebuilding soil, re-vegetating spoil, stabilising slopes and returning the land toward a self-sustaining ecosystem. This is the most ambitious objective and, as the Tamil Nadu case studies show, the one with the greatest reputational and ecological upside.

Major Technical Challenges

The gap between a green belt on paper and a green belt on the ground is filled with technical challenges specific to the cement environment. The following sections diagnose them in the order a landscape architect would assess a site: soil, water, plant survival, climate and operations.

Soil-related challenges

Alkalinity from cement dust. The most distinctive and best-documented soil problem at cement plants is progressive alkalinisation. Continuous deposition of alkaline cement dust raises soil pH; a peer-reviewed gradient study around cement plants recorded naturally acidic soils (pH 4.4–5.5) shifting to slightly alkaline (pH 6.7–7.2) closer to the plant, accompanied by falling organic carbon (from around 2.5 per cent to as low as 1.3 per cent), declining total nitrogen, reduced water-holding capacity and increased bulk density — a signature of compaction (Lamare & Singh, 2020). High pH locks up iron, manganese, phosphorus and other nutrients, producing chlorosis and stunting even where water is adequate.

Dust encrustation. Beyond the soil, deposited cement dust forms a hydrated calcium-silicate crust on leaves and soil surfaces that sets hard, sealing the soil surface against infiltration and clogging stomata so that gas exchange and photosynthesis are impaired (secondary review in Section references). Newly planted saplings, with limited leaf area and shallow roots, are especially vulnerable.

Poor organic matter, compaction and rocky or overburden substrata. Cement-plant soils are frequently construction-disturbed, scraped, compacted by heavy plant, thin over rock, or composed entirely of mine overburden and spoil with negligible organic matter, poor structure and low water-holding capacity. These substrates neither hold water nor supply nutrients and physically resist root penetration — the single biggest reason first-year saplings fail on quarry-rehabilitation sites.

Water-related challenges

Scarcity and seasonality. Most South Indian cement plants sit in semi-arid, hard-rock terrain where water is scarce, groundwater is stressed and rainfall is concentrated in a short monsoon. The belt must be established through long dry seasons when demand is highest and supply lowest.

Salinity and recycled water. Plants increasingly, and rightly, irrigate green belts with treated sewage or process water to avoid competing with drinking supplies. This water is often saline or sodic and must be managed: FAO guidance treats irrigation water below about 0.7 dS/m as unrestricted, 0.7–3.0 dS/m as requiring management and above 3.0 dS/m as severely restrictive, with sodium hazard assessed through the sodium adsorption ratio (Ayers & Westcot, 1985). Continuous irrigation with poor-quality water can itself salinise the root zone if drainage and leaching are not managed.

Irrigation limitations. Large perimeter belts and remote mine-rehabilitation areas are hard and expensive to irrigate uniformly; pressure losses, clogged emitters, vandalism and the sheer length of runs all conspire to leave parts of the belt under-watered while others are drowned.

Plant survival issues

Heat and dust stress. Young plants face combined heat, dust and wind stress that mature trees shrug off. Leaf temperatures rise, dust-clogged stomata cannot cool the plant by transpiration, and growth stalls.

Poor establishment. The first two to three years are decisive. Saplings planted too small, too deep, in unimproved pits, without staking, mulching or reliable water frequently die in the first summer, and a belt that loses a large fraction of its plants in year one rarely recovers its intended density.

Grazing and human interference. Cattle and goat grazing, browsing, trampling, firewood collection and encroachment are among the most common — and most underestimated — causes of plantation failure, particularly on unfenced peripheral belts and mine areas adjoining villages.

Climate challenges

High summer temperatures, intense solar radiation, hot desiccating winds, recurrent drought and, increasingly, erratic and extreme rainfall all test the belt. Climate variability widens the range of stresses the planting must tolerate, which is a direct argument for species and structural diversity rather than a single “best” species.

Operational challenges

A cement plant is a live, expanding industrial site. Heavy vehicle movement damages edge planting; mechanical damage from maintenance and construction is routine; utility corridors, pipe racks and conveyor belts fragment the available planting ground and impose access and safety constraints; and expansion projects periodically consume land that was previously green belt, requiring compensatory planting elsewhere. Designing the belt around — and defending it from — these operational realities is as important as any horticultural decision.

Maintenance Challenges

If establishment is the first battle, maintenance is the long war — and it is the phase where most green belts are quietly lost. A plantation that is celebrated at inauguration and then left to fend for itself will thin out within a few seasons. The recurring maintenance challenges are as follows.

Weed management. Aggressive weeds — including invasive Prosopis juliflora and Lantana camara — compete with young plants for water, light and nutrients and, if unmanaged, can overwhelm a young belt entirely. Weeding is labour-intensive and unglamorous, and it is often the first task to be cut.

Irrigation continuity. Drip systems clog, pumps fail, lines are cut and schedules slip. A lapse of a few weeks in peak summer can undo two years of establishment.

Fertilisation and soil replenishment. Poor industrial soils need sustained organic input; a single application of compost at planting is not enough to carry a tree to self-sufficiency on spoil or alkaline ground.

Pruning, pest and disease control. Formative pruning, canopy management for windbreaks, and integrated management of pests and disease all require skilled, timely attention that a plant focused on cement production may not resource.

Labour, budget and monitoring. The deepest challenges are institutional: shortage of trained horticultural labour, maintenance budgets that shrink once the capital planting is complete, and monitoring that reports numbers planted rather than numbers surviving and thriving. Casualty replacement — replacing dead saplings each year to hold the belt at its design density — is frequently neglected. Where monitoring fails, gradual attrition goes unnoticed until the belt is visibly sparse and the survival rate has fallen well below the ~80 per cent that clearance conditions assume (Rajasekaran et al., 2019).

Species Selection Challenges

More plantations fail for wrong species selection than for almost any other single reason. A species that is cheap, available at the nursery and quick to plant is not necessarily a species that will survive alkaline dust, tolerate drought, resist grazing and filter particulate for thirty years. Three recurring choices define the outcome.

Native versus exotic

Native and locally adapted species are, as a rule, better suited to local soil, climate and rainfall, support more biodiversity, and demand less water and intervention once established. The CPCB guideline explicitly favours pollution-tolerant native species (CPCB, 1999). Exotics are sometimes chosen for fast screening or ornamental effect, but many of the “reliable” exotics used in industrial planting — most notoriously Prosopis juliflora — are invasive, displace native vegetation, offer little habitat value and are difficult to remove. The default should be native; exotics should be justified case by case and invasives excluded outright.

Fast-growing versus long-life species

Fast-growing species deliver quick screening and early carbon capture but are often short-lived, weak-wooded, thirsty and prone to wind and pest damage; long-lived structural species establish more slowly but form the durable backbone of the belt. The resolution is not to choose one over the other but to combine them — fast nurse species to provide early cover and shelter, interplanted with long-life natives that will dominate the mature canopy — and to plan for the eventual thinning of the nurse crop.

Monoculture versus mixed plantation

A single-species block is simpler to plant and manage, but it is ecologically fragile: one pest, one disease or one climatic extreme can defoliate the entire belt, and a monoculture supports minimal biodiversity and provides uneven filtering. A mixed, multi-layered plantation spreads risk, extends flowering and fruiting through the year for pollinators and birds, and combines species whose different leaf structures and canopy heights filter a wider range of particle sizes. Diversity is not an aesthetic preference here; it is the primary insurance policy for a belt that must survive decades of variable stress.

Landscape Design Considerations

Design is where ecological understanding becomes a buildable layout. A cement-plant green belt is not a hedge; it is a structured landscape system with distinct typologies deployed according to the source zones identified earlier.

Buffer plantation and the three-tier structure

The workhorse of industrial green-belt design is the multi-tier buffer: a deep band, ideally structured in three layers — tall, dense, dust-tolerant trees on the outer (source-facing) rows; a middle layer of medium canopy and fruiting or flowering trees; and an inner layer of shrubs and hedges — with a ground layer of grasses or covers to suppress soil dust and control erosion. This layered structure filters particles across a range of heights and sizes, attenuates noise, reduces wind and screens the view, and it is the form most consistently specified in Indian clearance conditions (a “three-tier green belt”; Shree Digvijay Cement, 2023).

Avenue and peripheral planting

Avenue planting along internal roads and approaches controls haul-road dust, provides shade for workers and vehicles, and defines the site’s circulation, while the peripheral green belt forms the continuous boundary band that satisfies the area requirement and separates the plant from its neighbours.

Windbreaks and shelterbelts

Where wind-driven dust from yards and quarries is the dominant problem, a windbreak or shelterbelt — a belt oriented across the prevailing wind, of graduated height and moderate permeability — reduces wind velocity to leeward and suppresses dust pick-up. A semi-permeable belt outperforms a solid wall of vegetation, which creates damaging turbulence; the design target is a belt that filters rather than blocks the wind.

Ecological corridors and biodiversity pockets

Linking belts and retained natural vegetation into continuous corridors allows fauna to move through the site, and setting aside biodiversity pockets — small groves of mixed native species, left relatively undisturbed — concentrates habitat value. These features cost little and transform the belt’s ecological performance.

Water integration: rainwater harvesting and stormwater

Good belts are designed with the water system, not against it. Contour trenches, swales, check dams and recharge pits within and upslope of the belt capture monsoon runoff, recharge groundwater and passively irrigate the planting; stormwater from paved areas can be directed to the belt as a resource rather than discharged as a problem. On mine-rehabilitation terraces this integration is essential to establishing vegetation on free-draining spoil.

Green belt width guidance

Belt width is a function of pollution load and the space available. The following ranges, drawn from Indian green-belt literature, are widely used as planning benchmarks; the correct width for any plant is set by its clearance conditions and site constraints.

Width ranges after Rajasekaran et al. (2019) and state green-belt guidelines; treat as planning benchmarks, not fixed mandates. Actual requirements are set by the plant’s EC and consent conditions.

Plant Selection Strategy for South Indian Cement Industries

The following palette is assembled for the hot, semi-arid, alkaline-dust conditions of the South Indian cement belt, drawing on air-pollution-tolerance and dust-capture studies from Indian industrial and urban settings and on established horticultural knowledge. The organising logic is structural: the tallest, densest, roughest-leaved and most pollution-tolerant species belong on the outer, source-facing rows; medium fruiting and flowering species form the middle; shrubs and hedges the inner edge; and grasses and covers the ground layer, especially on spoil and slopes. Native species are preferred throughout; known invasives are excluded.

Two consistent findings from the Indian evidence guide the choice. First, species with high Air Pollution Tolerance Index (APTI) values — repeatedly including Ficus benghalensis, Ficus religiosa, Azadirachta indica, Mangifera indica, Syzygium cumini and Peltophorum pterocarpum — sustain physiological function under pollutant load (Rai, 2016; CPCB, 1999). Second, dust capture is governed by leaf micro-morphology: rough, hairy, leathery and large leaves in dense canopies trap the most particulate, with Polyalthia longifolia, Tectona grandis, Butea monosperma, Ficus species, Pongamia pinnata and Azadirachta indica recording the highest foliar dust loads in Tamil Nadu and other Indian studies (Rai, 2016).

Rankings are indicative and site/season-dependent; APTI values for the same species vary between studies, so species are grouped as “consistently tolerant” rather than by fixed numeric scores (Rai, 2016; CPCB, 1999).

Indicative only; actual demand varies with soil, mulch, microclimate and season. The design intent is a belt that becomes largely self-sustaining by Year 3–4.

Irrigation Strategy

Water is the binding constraint on most South Indian cement-plant belts, so irrigation must be efficient, resilient and, wherever possible, based on recycled water. The strategy is a hierarchy: harvest and recharge first, apply water precisely second, and monitor to avoid both drought and waste.

Drip as the default; sprinklers by exception

Drip (micro-)irrigation is the default for green belts because it delivers water directly to the root zone at high efficiency and suits long, linear belts. FAO field-application efficiencies illustrate the case: surface irrigation achieves about 60 per cent, sprinklers about 75 per cent and drip about 90 per cent (FAO, n.d.). For a water-scarce site, the ~30 percentage-point advantage of drip over surface methods is decisive. Sprinklers have a role for turf and grassed slopes but waste water to evaporation in hot, windy conditions and are best avoided on the open belt.

Efficiencies after FAO irrigation-management guidance (FAO, n.d.).

Treated sewage and process water reuse

Irrigating the belt with treated sewage or process water conserves fresh water and is now standard good practice, but the water must be managed for salinity and pathogens. FAO thresholds treat irrigation water below about 0.7 dS/m as unrestricted, 0.7–3.0 dS/m as requiring management, and above 3.0 dS/m as severely restrictive, and set microbial limits for restricted and unrestricted reuse (Ayers & Westcot, 1985). Practical precautions include monitoring electrical conductivity and the sodium adsorption ratio, ensuring adequate drainage and periodic leaching to prevent salt build-up, and directing recycled water to non-amenity structural planting. Indian plants routinely irrigate green belts with treated effluent under pollution-control guidance; the specific consent limits for any plant should be confirmed with the State board.

Smart irrigation and rainwater harvesting

Soil-moisture sensors and IoT-based scheduling apply water only when and where the root zone needs it; field IoT precision-irrigation systems have cut water use by up to about 30 per cent while maintaining plant performance (Dong et al., 2024). Coupled with contour trenches, swales, check dams and recharge pits that capture monsoon runoff, smart scheduling turns a scarce and expensive input into a managed resource. On mine-rehabilitation terraces, rainwater harvesting is often the difference between success and failure on free-draining spoil.

Soil Improvement

Because cement-plant soils are alkaline, compacted, low in organic matter or composed of spoil, soil rehabilitation is not optional — it is the foundation on which survival rests. The programme begins with testing and proceeds through physical, chemical and biological improvement.

Soil testing and diagnosis

Every belt should begin with soil testing across the site — pH, electrical conductivity, organic carbon, nutrients, texture and, on quarry ground, the character of the spoil. Alkalinity and salinity gradients around the plant (Lamare & Singh, 2020) mean that a single specification cannot serve the whole belt; amendments must be matched to measured conditions zone by zone.

Amending alkaline and sodic soils

Where high pH and sodicity are the problem, gypsum is the established corrective: ICAR–CSSRI recommends of the order of 12–15 tonnes of gypsum per hectare for severely deteriorated alkali soils to reclaim the topsoil, working by replacing exchangeable sodium with calcium, with the dose reduced when combined with farmyard manure and followed by ponding to leach sodium (ICAR–CSSRI, n.d.). Incorporating abundant organic matter alongside gypsum both buffers pH and rebuilds structure.

Organic matter: compost, vermicompost, mulching and biochar

Rebuilding organic carbon is the single most valuable intervention on poor industrial soils. Compost and vermicompost supply nutrients and improve structure and water-holding capacity — a meta-analysis found vermicompost raised plant growth substantially, with optimal effects at roughly a third to a half of the growing medium (Blouin et al., 2019). Mulching the root zone conserves moisture, suppresses weeds and moderates soil temperature, all critical in the first summers. Biochar merits particular attention on cement sites: meta-analyses report consistent, durable improvements in yield and water retention, strongest on coarse-textured and neutral-to-acidic soils, and larger still when biochar is combined with fertiliser (biochar meta-analysis summary, n.d.). Its liming and water-holding effects and long persistence make it well suited to spoil and degraded ground.

Biological inoculation: mycorrhiza and biofertilisers

Living soil biology accelerates establishment on hostile substrates. Arbuscular mycorrhizal fungi extend the effective root system, improving phosphorus and water uptake and conferring drought, salinity and heavy-metal tolerance, while their glomalin improves soil structure — making them especially valuable on mine spoil and rocky substrata (Samanta et al., 2025). Nitrogen-fixing biofertilisers such as Rhizobium (with leguminous species like Pongamia, Albizia and Dalbergia) add biologically fixed nitrogen — Rhizobium can fix on the order of 50–100 kg N per hectare and raise legume performance (Bahuguna et al., 2025) — and phosphate-solubilising and free-living nitrogen-fixing microbes further reduce fertiliser dependence. Pairing nitrogen-fixing tree species with inoculation is a powerful, low-cost strategy for spoil rehabilitation.

Maintenance Best Practices

Maintenance is where green belts are won or lost. The following protocol frames aftercare as a scheduled, resourced, multi-year programme rather than an afterthought, with the intensity front-loaded into the decisive first three years and a defined five-year horizon to self-sufficiency.

Integrated pest management and pruning

Pest and disease pressure should be managed through integrated pest management — monitoring, encouraging natural enemies, cultural controls and targeted, minimal chemical intervention only when thresholds are exceeded — which suits the biodiverse ethos of the belt and avoids harming pollinators. Formative and structural pruning shapes shade trees along avenues, maintains the semi-permeable profile of windbreaks and removes dead or damaged wood.

Casualty replacement and record-keeping

The most under-resourced maintenance task is casualty replacement — annually replanting dead saplings to hold the belt at its design density — without which even a well-established belt slowly thins below its clearance survival target. Disciplined record-keeping (numbers planted, species, locations, survival, replacements) turns the belt into a managed asset and provides the geotagged, auditable evidence regulators increasingly require (UltraTech Cement, 2025).

Technology Integration

Technology has transformed green-belt monitoring from an annual walkover into a continuous, spatially precise, evidence-based process — and it is increasingly what regulators expect.

GIS and satellite monitoring with NDVI. Geographic Information Systems record every planting location, species and survival status as a living spatial database, while satellite and drone imagery feed the Normalised Difference Vegetation Index (NDVI) — a measure of vegetation vigour that reveals healthy versus stressed or failed planting across the whole belt. Forest agencies in India already use GIS, satellite and drone NDVI to compare planned versus actual plantation and to flag canopy loss (Esri India, n.d.).

Drone and UAV survey. Multispectral drones survey large, difficult-access belts and mine terraces quickly, distinguishing surviving trees from failed patches and generating the geotagged imagery now used in half-yearly compliance reporting. UAV survival-monitoring methods are established in the afforestation literature and are directly applicable to arid cement-site rehabilitation.

IoT sensors and smart management. In-field soil-moisture and micro-climate sensors drive precision irrigation, cutting water use materially (Dong et al., 2024) and giving early warning of drought stress. Integrated with a GIS dashboard, sensor and imagery data create a digital twin of the belt for management.

AI-assisted monitoring. Machine-learning analysis of multispectral drone and satellite data automates tree counting, species classification, health assessment and change detection, and emerging AI-driven monitoring is being applied specifically to afforestation in arid environments — precisely the conditions of South Indian cement sites. The value is a shift from reporting numbers planted to demonstrating, with evidence, numbers surviving and thriving.

Biodiversity Enhancement

A green belt designed for biodiversity delivers far more than one designed only to screen. Modest, deliberate additions convert the belt into functioning habitat and materially improve its ESG value, which international operators now measure formally (Holcim, n.d.).

Pollinator corridors and butterfly gardens. Sequencing nectar and host plants — Cassia, Bauhinia, Ixora, Lantana-alternatives, Calotropis (a butterfly host), flowering shrubs and native grasses — so that something is in flower year-round sustains bees and butterflies and, with them, the wider food web.

Bird and small-fauna habitat. Native fruiting trees (Ficus, Syzygium, Mangifera), varied canopy heights and undisturbed groves provide food and nesting; Ficus species in particular are keystone resources supporting a disproportionate range of birds and insects.

Native grasses and wetland or water features. Native grass understoreys stabilise soil and feed insects, while harvested-water ponds and constructed wetlands within the belt add aquatic habitat and support amphibians, dragonflies and birds — turning stormwater management into biodiversity gain.

Ecological restoration of mined land. The greatest biodiversity opportunity is the mined-out quarry. Dense native planting — including Miyawaki-style plots that establish fast, high-diversity groves — terracing, re-soiling and re-grassing can return spoil toward a self-sustaining native ecosystem, as demonstrated at Tamil Nadu and other Indian cement operations (see Case Studies).

Climate Change Adaptation

A green belt planted today must survive a hotter, more variable climate over its decades-long life, and it is itself one of the plant’s most credible climate responses. The design principles that make a belt resilient are the same ones that make it a nature-based climate solution.

Carbon sequestration as mitigation. The maturing belt is a growing carbon store that partially offsets the plant’s largely unavoidable process emissions and contributes to net-zero commitments; species and density choices should consider long-term carbon alongside filtration and biodiversity (Kaul et al., 2011).

Heat and drought resilience. Diversity is the core adaptation strategy: a belt of many species, ages and structures is far more likely to withstand a novel pest, an extreme drought or an unseasonal deluge than a uniform block. Drought-hardy natives, deep improved soils, mulching and rainwater harvesting build resilience into the system, while shade and transpiration from the belt itself buffer the site against rising heat.

Water conservation and nature-based solutions. Recycled-water irrigation, smart scheduling and rainwater harvesting reduce the belt’s demand on stressed supplies, and the belt’s swales, trenches and wetlands are themselves nature-based solutions that recharge groundwater and moderate flood and drought extremes. Framed this way, the green belt is not a cost of compliance but part of the plant’s climate-adaptation infrastructure.

Case Studies

The following examples are drawn from documented company and regulatory sources. Tamil Nadu cases are given first, then Indian and international examples for breadth. Where plant-specific figures could not be independently verified, this is stated rather than assumed.

Tamil Nadu: the Ariyalur cement belt in context

Ariyalur district is officially styled the “Land of Cements.” The district administration records seven cement plants and dozens of major-mineral limestone leases concentrated in the Ariyalur–Perambalur belt, with limestone, lime-kankar and marl as the principal raw materials (Ariyalur District Administration, n.d.). This makes the belt Tamil Nadu’s epicentre for cement production, limestone quarrying and — necessarily — for industrial green-belt and mine-rehabilitation work under a hot, semi-arid, alkaline-dust regime.

Case 1 — The Ramco Cements Eco Park, Pandalgudi (Virudhunagar district)

The strongest documented Tamil Nadu case is The Ramco Cements’ ecological restoration of its mined-out limestone quarry at Pandalgudi. Reported accounts describe an 800-acre restoration programme, with roughly 350 acres completed in phases, transforming worked-out limestone dumps into an “Eco Park” through terracing of 30-metre benches, Miyawaki-style dense native planting, an in-house indigenous nursery, and rockery gardens built from waste stone. The programme reports around 2.5 lakh (250,000) saplings planted toward a one-million target, spanning some 250 species of which about 150 are indigenous — including Ficus species, neem, peepal, Pongamia, Mimusops (magizham) and medicinal and dry-evergreen species — together with a butterfly garden, an environmental-education centre and around 18 kilometres of walking and cycling trails; the park was inaugurated in March 2022 (Construction World, 2022). It is a model of how a liability — an exhausted quarry — can be converted into a biodiversity and community asset.

Case 2 — UltraTech Reddipalayam Cement Works, Ariyalur district

UltraTech’s Reddipalayam works illustrates green-belt and mine-boundary planting under formal compliance monitoring. The plant’s environmental-clearance compliance reporting for its Periyanagalur limestone mine documents around 3,800 native-species saplings (over six feet at planting) established along a 7.5-metre safety zone around the mine boundary for fugitive-dust capture, carbon sequestration and noise attenuation, with a final mine-closure plan including re-grassing and a biodiversity study submitted to the District Forest Officer in October 2025, and GPS coordinates and photographs filed with the State board and appraisal authority (UltraTech Cement, 2025). It demonstrates the shift toward evidenced, geotagged, regulator-facing green-belt monitoring.

Case 3 — Other Tamil Nadu plants (Dalmia, India Cements, Chettinad, TANCEM)

Other major Tamil Nadu operators — Dalmia Bharat Cement at Dalmiapuram (Ariyalur), the long-established India Cements works at Sankarnagar (Tirunelveli) and its Sankari and Dalavoi units, Chettinad Cement at Puliyur (Karur), and the state-owned TANCEM units at Ariyalur and Alangulam — all list green-belt development and tree-planting among their environmental priorities and carry formal green-belt plans within their clearance filings. Plant-specific tree counts and green-belt areas for these sites were not independently verifiable from public sources at the time of writing and should be obtained directly from each plant’s TNPCB consent and EC compliance documents before being cited as figures. They are noted here to place the anchor cases within the fuller Tamil Nadu picture.

Indian examples for breadth

Beyond Tamil Nadu, Dalmia Cement has developed roughly one-hectare Miyawaki dense native plantations in mine areas (reported at its Kadapa operation in Andhra Pradesh), which establish far faster and denser than conventional planting and become largely maintenance-free after about three years (GCCA, 2021); the same group reported planting tens of thousands of saplings across plant, colony and mining areas in a single 2025 drive (The Hans India, 2025). At group scale, Ambuja Cements and ACC report having planted around 1.5 million trees, with a target of 8.3 million by 2030 across the portfolio, alongside compensatory afforestation and land reclamation from waste operations (Ambuja Cements, 2025). These illustrate both the Miyawaki method and the scale at which the sector now operates.

International example

Internationally, Holcim has developed a Biodiversity Indicator and Reporting System with the International Union for Conservation of Nature (IUCN) and reports having established a biodiversity baseline across all of its active and non-active quarries, with a commitment to a measurable net-positive biodiversity impact by 2030 and progressive rehabilitation of worked-out areas (Holcim, n.d.). It points toward the measurement-led future of quarry and green-belt biodiversity that Indian operators are increasingly adopting.

Common Mistakes: 25 Reasons Industrial Plantations Fail

Distilled from the challenges above and from field experience, the following are the most frequent reasons cement-plant green belts underperform. Most are avoidable with better diagnosis, design and aftercare.

1. Treating planting as an event, not a decade-long process — celebrating the first planting and under-resourcing everything after.
2. Wrong species for the site — choosing on availability or cost rather than tolerance to dust, drought and alkalinity.
3. Monoculture planting — leaving the whole belt exposed to a single pest, disease or climatic extreme.
4. Over-reliance on fast-growing exotics that are short-lived, weak or thirsty.
5. Planting known invasives such as Prosopis juliflora or Lantana camara.
6. Ignoring soil pH and alkaline dust — planting into un-amended alkaline, sealed soil.
7. No soil testing — a uniform specification applied to a site with strong gradients.
8. Failing to rebuild organic matter — one dose of compost expected to last a lifetime.
9. Compacted or un-ripped ground — roots that cannot penetrate the substrate.
10. Planting directly into raw mine spoil without soil-building or inoculation.
11. Poor-quality or oversized/undersized nursery stock, or root-bound saplings.
12. Planting too deep or in undersized pits.
13. Wrong planting season — missing the monsoon window and facing summer at once.
14. Inadequate irrigation design — runs too long, pressure too low, no filtration for recycled water.
15. Irrigation lapses in peak summer that undo two years of establishment.
16. Salinity build-up from recycled water without leaching or drainage.
17. No mulching — moisture lost, weeds rampant, soil overheated.
18. Weeds left uncontrolled in the critical establishment years.
19. No protection from grazing and trampling — unfenced belts browsed to failure.
20. Human interference — encroachment, firewood collection, fire.
21. Neglecting casualty replacement — the belt slowly thins below its survival target.
22. Insufficient belt width or gaps that let dust, noise and wind pass through.
23. Wrong placement relative to sources and wind — dense species in the wrong rows.
24. No monitoring, or monitoring the wrong metric — counting trees planted, not trees surviving.
25. Maintenance budget cut once capital planting is done — the commonest institutional failure of all.

Practical Recommendations: A Project Manager’s Checklist

The following checklist condenses the article into the sequence a plant should follow to build a green belt that survives and performs.

Plan & diagnose

• Confirm the EC/consent conditions (area %, density, species, survival target) and map them against available land.
• Map the plant’s source zones (crusher, yards, kiln, packing, haul roads, quarry) and the prevailing wind and sensitive receptors.
• Carry out site-wide soil testing (pH, EC, organic carbon, nutrients, texture, spoil character).
• Confirm the water source, quantity and quality (fresh vs. recycled; EC and SAR) for the belt.

Design

• Design a three-tier buffer with dust-tolerant structural species on source-facing rows; add avenues, windbreaks, corridors and biodiversity pockets.
• Select a diverse, mostly-native palette matched to each zone; exclude invasives; combine nurse and long-life species.
• Integrate rainwater harvesting (trenches, swales, recharge pits) and design efficient drip irrigation with filtration.
• Plan mine-rehabilitation terraces and dense native/Miyawaki planting where applicable.

Establish

• Rip/pit hostile ground; amend soil (gypsum for alkalinity, compost/vermicompost, biochar, AMF and biofertilisers).
• Use quality stock, correct planting depth, staking, tree guards and mulch; plant into the monsoon window.
• Fence and protect against grazing and encroachment from day one.

Maintain, monitor & report

• Resource a multi-year maintenance contract (irrigation, weeding, IPM, pruning, fertilisation) — front-loaded to years 1–3.
• Replace casualties annually to hold design density; keep species/location/survival records.
• Monitor with GIS, drone/NDVI and soil sensors; evaluate against the survival target; report with geotagged evidence.
• At year five, thin nurse species, enrich weak zones and transition drought-hardy planting to rain-fed.

Conclusion

Green belt development in the cement industry is simultaneously a legal obligation, an ecological opportunity and a technical challenge that is routinely underestimated. The obligation is clear: environmental clearances require a substantial, dense, native, surviving green belt, and the regulatory direction of travel is toward verified, monitored green cover rather than nominal area. The opportunity is equally clear: a well-designed belt filters fugitive dust, sequesters carbon, attenuates noise, cools the site, screens the plant, harvests water and rebuilds biodiversity — turning the most emissions-intensive of industries a little back toward the ecosystem it sits within.

The challenge is where most plants stumble. Alkaline dust, water scarcity, hostile soils, heat, grazing and the churn of a live industrial site conspire against young plants, and a green belt treated as a one-off planting event will thin and fail. The evidence and practice reviewed here point to a different approach: diagnose the site zone by zone; match diverse, mostly-native species to the specific stresses of each; engineer the soil and water systems that survival depends on; and, above all, resource and monitor a multi-year programme of aftercare with casualty replacement and modern, evidence-based monitoring. The Tamil Nadu case studies — Ramco’s Eco Park at Pandalgudi and UltraTech’s monitored mine-boundary planting at Reddipalayam in the Ariyalur belt — show what is achievable when a plant commits to restoration rather than mere compliance.

For a landscape-architecture practice, this is the essential message to carry to cement-plant management: the difference between a failed plantation and a thriving green belt is not the budget for saplings but the quality of design, soil and water engineering, species selection and long-term care. Invest there, and the green belt becomes exactly what regulation intends and what the surrounding community deserves — a durable, living buffer that protects air, land, water and people for decades.

---

Appendix A — Additional Reference Tables

Structure only — actual figures depend on belt area, site condition and water source, and should be built into the EMP budget at the clearance stage.

---

References

Reference list curated for verifiability: every source below is a real, accessible document. A small number of journal papers whose full author lists could not be confirmed from the source page are marked accordingly rather than guessed. Foundational and standards references (e.g., Singh & Rao, 1983; ISO 14001) are widely established works in the field.

1. Ambuja Cements Ltd. (2025). Natural capital — Integrated annual report 2024-25. https://www.ambujacement.com/annual-report-2024/natural-capital.html
2. Andrew, R. M. (2019). Global CO₂ emissions from cement production, 1928–2018. Earth System Science Data, 11(4), 1675–1710. https://essd.copernicus.org/articles/11/1675/2019/
3. Ariyalur District Administration. (n.d.). Geology & mining — Ariyalur District, Government of Tamil Nadu. https://ariyalur.nic.in/departments/geology-mining/
4. Ayers, R. S., & Westcot, D. W. (1985). Water quality for agriculture (FAO Irrigation and Drainage Paper 29, Rev. 1). Food and Agriculture Organization of the United Nations. https://www.fao.org/4/t0551e/t0551e04.htm
5. Bahuguna, A., et al. (2025). Rhizobium as a potential biofertilizer and its quality control analysis for sustainable agriculture. Journal of Applied Biology & Biotechnology, 13(3), 97–105. https://jabonline.in/admin/php/uploads/1327_pdf.pdf
6. Beckett, K. P., Freer-Smith, P. H., & Taylor, G. (1998). Urban woodlands: Their role in reducing the effects of particulate pollution. Environmental Pollution, 99(3), 347–360.
7. Beckett, K. P., Freer-Smith, P. H., & Taylor, G. (2000). Particulate pollution capture by urban trees: Effect of species and windspeed. Global Change Biology, 6(8), 995–1003.
8. Bihar State Pollution Control Board. (n.d.). Guidelines for green belt development. BSPCB. https://bspcb.bihar.gov.in/Guidelines%20for%20green%20belt%20%20development.pdf
9. Blouin, M., Barrere, J., Meyer, N., Lartigue, S., Barot, S., & Mathieu, J. (2019). Vermicompost significantly affects plant growth: A meta-analysis. Agronomy for Sustainable Development, 39, 34. https://link.springer.com/article/10.1007/s13593-019-0579-x
10. Bureau of Indian Standards. (n.d.). IS 5182: Methods for measurement of air pollution [standard series]. BIS.
11. Central Pollution Control Board. (1999). Guidelines for developing greenbelts (PROBES/75/1999–2000). Ministry of Environment & Forests, Government of India. https://dste.py.gov.in/ppcc/pdf/Guidelines/Greenbelts.pdf
12. Central Pollution Control Board. (2009). National ambient air quality standards (Notification No. B-29016/20/90/PCI-L, 18 November 2009). MoEF, Government of India. https://cpcb.nic.in/air-quality-standard/
13. Chavan, B. L., & Rasal, G. B. (2011). Sequestered standing carbon stock in selective tree species grown in university campus at Aurangabad, Maharashtra, India. International Journal of Engineering Science and Technology, 3(4), 3003–3007.
14. Construction World. (2022). Ramco Eco Park. https://www.constructionworld.in/resources-company-news/ramco-eco-park/32939
15. Dong, Y., et al. (2024). Implementation of an in-field IoT system for precision irrigation management. Frontiers in Water, 6, 1353597. https://www.frontiersin.org/journals/water/articles/10.3389/frwa.2024.1353597/full
16. Down To Earth. (2026, April 17). Daily court digest: Major environment orders (cement-plant violations, Haryana). https://www.downtoearth.org.in/environment/daily-court-digest-major-environment-orders-april-17-2026
17. ESG Broadcast. (2025). India’s MoEFCC revised industrial green belt / green cover criteria based on pollution potential. https://esgbroadcast.com/broadcast/indias-moefcc-revised-industrial-green-belt-green-cover-criteria-based-on-pollution-potential/
18. Escobedo, F. J., & Nowak, D. J. (2009). Spatial heterogeneity and air pollution removal by an urban forest. Landscape and Urban Planning, 90(3–4), 102–110.
19. Esri India. (n.d.). How GIS and drone data transform forest management. https://www.esri.in/en-in/newsroom/blog/how-gis-drone-data-transforms-forest-management
20. Food and Agriculture Organization of the United Nations. (n.d.). Irrigation water management: Irrigation methods (Annex I: Irrigation efficiencies). FAO. https://www.fao.org/4/t7202e/t7202e08.htm
21. Freer-Smith, P. H., Beckett, K. P., & Taylor, G. (2005). Deposition velocities to Sorbus aria, Acer campestre, Populus deltoides × trichocarpa, Pinus nigra and ×Cupressocyparis leylandii for coarse, fine and ultra-fine particles in the urban environment. Environmental Pollution, 133(1), 157–167.
22. Global Cement and Concrete Association. (2021). Measures taken to enhance biodiversity by Dalmia Cement. GCCA. https://gccassociation.org/about-us/our-members/member-spotlight/measures-taken-to-enhance-biodiversity-by-dalmia-cement/
23. Global Cement and Concrete Association. (2025). Global cement industry reports 25% CO₂ intensity reduction. GCCA. https://gccassociation.org/news/global-cement-industry-reports-25-co2-intensity-reduction-and-calls-for-urgent-government-action-to-accelerate-net-zero-mission/
24. Global Energy Monitor. (n.d.). India Cements Sankarnagar cement plant. https://www.gem.wiki/India_Cements_Sankarnagar_Cement_Plant
25. Holcim Ltd. (n.d.). Biodiversity. https://www.holcim.com/sustainability/nature/biodiversity
26. ICAR–Central Soil Salinity Research Institute. (n.d.). Reclamation of alkali soils through gypsum technology. ICAR-CSSRI, Karnal. https://cssri.res.in/poxumyse/2023/05/2016-01-Reclamation-of-Alkali-Soils-through-Gypsum-Technology.pdf
27. Intergovernmental Panel on Climate Change. (2022). Climate change 2022: Mitigation of climate change (Working Group III contribution to the Sixth Assessment Report). Cambridge University Press.
28. International Energy Agency. (2018). Technology roadmap: Low-carbon transition in the cement industry. IEA. https://iea.blob.core.windows.net/assets/cbaa3da1-fd61-4c2a-8719-31538f59b54f/TechnologyRoadmapLowCarbonTransitionintheCementIndustry.pdf
29. International Organization for Standardization. (2015). ISO 14001:2015 — Environmental management systems: Requirements with guidance for use. ISO.
30. Janhäll, S. (2015). Review on urban vegetation and particle air pollution — Deposition and dispersion. Atmospheric Environment, 105, 130–137.
31. Kaul, M., Mohren, G. M. J., & Dadhwal, V. K. (2011). Carbon storage and sequestration potential of selected tree species in India. Mitigation and Adaptation Strategies for Global Change, 16(2), 155–168. https://link.springer.com/article/10.1007/s11027-010-9230-5
32. Lamare, R. E., & Singh, O. P. (2020). Effect of cement dust on soil physico-chemical properties around cement plants in Jaintia Hills, Meghalaya. Environmental Engineering Research, 25(3), 409–417. https://www.eeer.org/journal/view.php?viewtype=pubreader&number=1060
33. Leghari, S. K., & Zaidi, M. A. (2013). Effect of air pollution on the leaf morphology of common plant species of Quetta city. Pakistan Journal of Botany, 45(S1), 447–454.
34. Ministry of Environment and Forests. (2006). Environmental Impact Assessment Notification, 2006 (S.O. 1533(E), 14 September 2006). Government of India. https://www.ielrc.org/content/e0654.pdf
35. Nguyen, T. L., et al. (2021). Noise pollution and occupational noise-induced hearing loss in cement plants in Vietnam. International Journal of Environmental Research and Public Health, 18(8), 4229. https://www.mdpi.com/1660-4601/18/8/4229
36. Nowak, D. J., Crane, D. E., & Stevens, J. C. (2006). Air pollution removal by urban trees and shrubs in the United States. Urban Forestry & Urban Greening, 4(3–4), 115–123.
37. Plants of the World Online. (n.d.). Chrysopogon zizanioides (L.) Roberty. Royal Botanic Gardens, Kew. https://powo.science.kew.org/taxon/urn:lsid:ipni.org:names:396213-1
38. Plants of the World Online. (n.d.). Pongamia pinnata (L.) Pierre. Royal Botanic Gardens, Kew. https://powo.science.kew.org/taxon/urn:lsid:ipni.org:names:515679-1
39. Prajapati, S. K., & Tripathi, B. D. (2008). Seasonal variation of leaf dust accumulation and pigment content in plant species exposed to urban particulates. Journal of Environmental Quality, 37(3), 865–870.
40. Rai, P. K. (2016). Impacts of particulate matter pollution on plants: Implications for environmental biomonitoring. Ecotoxicology and Environmental Safety, 129, 120–136. https://www.sciencedirect.com/science/article/abs/pii/S0147651316300719
41. Rajasekaran, A., et al. (2019). Green belt requirement for new and expansion projects. International Journal of Applied Environmental Sciences, 14(5). https://www.ripublication.com/ijaes19/ijaesv14n5_04.pdf [author list to be confirmed]
42. Samanta, S., et al. (2025). Arbuscular mycorrhizal fungi — a natural tool to impart abiotic stress tolerance in plants. Plant Signaling & Behavior, 20(1), 2525843. https://www.tandfonline.com/doi/full/10.1080/15592324.2025.2525843
43. Securities and Exchange Board of India. (2021). Business Responsibility and Sustainability Reporting (BRSR). SEBI.
44. Shree Digvijay Cement Company Ltd. (2023). Environmental clearance — Expansion of cement plant & clinker with WHRS [Government EC letter, Schedule item 3(b)]. https://www.digvijaycement.com/wp-content/uploads/2023/11/Environmental-Clearance-%E2%80%93-Expansion-of-Cement-Plant-Clinker-with-WHRS.pdf
45. Singh, S. K., & Rao, D. N. (1983). Evaluation of plants for their tolerance to air pollution. In Proceedings of the Symposium on Air Pollution Control (pp. 218–224). Indian Association for Air Pollution Control.
46. The Hans India. (2025, September 19). Dalmia Cement plants 30K trees. https://www.thehansindia.com/news/national/dalmia-cement-plants-30k-trees-1007799
47. Tree-Nation. (n.d.). How much CO₂ does a tropical tree sequester? [Report]. https://www.truevaluemetrics.org/DBpdfs/Forests/Tree-Nation-Tropical-tree-sequestration-of-CO2.pdf
48. UltraTech Cement Ltd. (2025). Environmental clearance compliance report, Reddipalayam Cement Works — Limestone Mine ML-5. https://www.ultratechcement.com/content/dam/ultratechcementwebsite/pdf/sustainability-new/state/tamil-nadu/environment-compliance/reddipalayam-cement-works/RDCW-EC-ECCR-2025-26-H1-Limestone%20Mine%20ML%205%20(8863).pdf
49. United States Environmental Protection Agency. (n.d.). What are heat islands? EPA. https://www.epa.gov/heatislands/what-are-heat-islands
50. United States Environmental Protection Agency. (n.d.). Using trees and vegetation to reduce heat islands. EPA. https://www.epa.gov/heatislands/using-trees-and-vegetation-reduce-heat-islands
51. World Economic Forum. (2024, September). 4 ways to make the cement industry more sustainable. WEF. https://www.weforum.org/stories/2024/09/cement-production-sustainable-concrete-co2-emissions/
52. World Health Organization. (2021). WHO global air quality guidelines: Particulate matter (PM2.5 and PM10), ozone, nitrogen dioxide, sulfur dioxide and carbon monoxide. WHO. https://www.who.int/publications/i/item/9789240034228

---