Urban sanitation and waste law in India begins with an absence. A resident who wants to know which statute obliges the municipality to collect the garbage from the lane, which statute obliges the household to separate it first, and which statute punishes either of them for failing, will search the statute book in vain, because no Parliament has enacted a sanitation Act and no central legislation on solid waste management exists. What exists instead is a body of rules, made by the Union executive under a general environmental protection statute of 1986, laid over a foundation of State municipal law that the rules do not amend and cannot fund. The duties of daily life in this field, who must segregate, who must collect, who must process, who must pay, are found in subordinate legislation, in municipal bye-laws made under State Acts, and in the directions of a tribunal. The statute book is silent at exactly the point where the subject touches every household in the country every day.

That structure is the subject of this article, and it produces a consequence the reader should hold from the outset. Because the operative instrument is a set of rules made under an environmental Act, the duties fall on municipalities under an instrument that provides them no money, and on residents under an instrument that almost nobody enforces. The claim can be stated as the article’s organising proposition: sanitation law without a sanitation statute means that the instrument which creates the duty, the instrument which provides the money and the instrument which enforces the sanction are three different instruments answering to three different authorities. The rules that create the duties are made in Delhi under the Environment (Protection) Act, 1986. The money, such as it is, arrives through State budgets and through a Union sanitation mission that is a scheme rather than a law. The sanction, when it moves at all, moves through State pollution control boards and through the National Green Tribunal, neither of which answers to the residents who live with the uncollected waste. Everything in the pages that follow is an elaboration of that triangle.

The article is built for three readers in particular. The resident and the residents’ association will find the duties that bind a household, the user fee the municipality may charge, the spot fine that exists on paper, and the route a complaint actually travels. The municipal official will find the full catalogue of obligations the rules impose on a local body, the timelines attached to them, and the enforcement exposure that follows when they are missed. The researcher will find the mismatch analysis: why a Union rulebook governs a State subject, why the enforcement runs to a tribunal rather than to a department, and what a sanitation statute would have to do that rules cannot. The treatment follows the discipline of a statute pillar even though the subject is a body of rules, because the Solid Waste Management Rules, 2016 are the closest thing this field has to a principal Act, and they cannot be understood without the parent statute above them, the municipal law beneath them and the parallel rulebooks beside them.

The municipal base: sanitation law before the rules

The first layer of the subject is older than environmental law and has nothing to do with the Union. Public health and sanitation is a State subject. Entry 6 of the State List in the Seventh Schedule assigns public health and sanitation, hospitals and dispensaries to the State legislatures, and Entry 5 of the same List assigns local government, meaning the constitution and powers of municipal corporations and other local authorities for the purpose of local self-government or village administration. The municipal Acts of the States, the corporation Acts of the great cities and the municipalities Acts of the smaller towns, are where sanitation first appears as law: as a list of obligatory functions cast on the municipal body, covering the cleansing of streets, the removal and disposal of refuse, the construction and maintenance of drains and sewers, the provision of public conveniences and the abatement of nuisances. A municipality in India does not derive its duty to clean the streets from the Solid Waste Management Rules. It derives that duty from its own State Act, which typically makes cleansing and refuse disposal an obligatory rather than discretionary function, and finances it, in the design if not always in the result, out of municipal taxation, principally the property tax.

This matters to everything that follows, because the State Act also fixes the municipality’s revenue handles, its staffing, its borrowing and the State government’s powers of supervision and supersession over it. The Union rules of 2016 were laid on top of institutions whose legal personality, money and personnel are entirely creatures of State law. The rules could command the institution. They could not reach inside it and alter what it is.

Is sanitation a subject for the States or for the Union?

Sanitation sits in the State List: Entry 6 covers public health and sanitation, and Entry 5 covers local government itself. The Union enters through a different door, the power to implement international agreements and the environmental statute built on it, which is why the duties arrive dressed as environmental rules rather than as a sanitation code.

The courts fastened the municipal duty long before any rulebook existed. In Municipal Council, Ratlam v. Vardhichand, decided in 1980, residents of Ratlam in Madhya Pradesh complained of open drains, slums without sanitation and a public nuisance the municipality had failed to abate, and the Supreme Court treated the municipal body’s statutory duty to provide sanitation as enforceable against it. The holding that has echoed through every waste case since is the rejection of the plea of poverty: a municipality could not plead financial inability to escape a duty its own statute imposed, because the duty was owed to the public and the budget had to be ordered around it. The Ratlam principle supplies the moral grammar of the whole field. The obligation is the municipality’s; the want of money is the municipality’s problem to solve within the law, not a defence against the resident. What Ratlam could not supply, and what no judgment can supply, is the money itself, and the distance between the principle and the purse is the space in which the modern rules operate.

The municipal base also explains a feature of the subject that surprises readers who approach it from the rules alone. The household’s obligations, the fee for collection, the penalty for littering, are not in the central rules in any directly enforceable form. They live in municipal bye-laws, which each local body frames under its State Act and under the prodding of the central rules, and bye-laws differ from city to city in their amounts, their machinery and their seriousness. There is no national fine for littering, whatever popular writing on the subject asserts. There are several thousand local fine regimes of wildly varying quality, most of them dormant. The central rules set the template; the bye-law is the operative instrument against the resident; and the gap between template and instrument is one of the recurring facts of this field.

The litigation that produced a national rulebook

The national rulebook exists because the Supreme Court spent the better part of two decades supervising municipal garbage. In 1996 two proceedings set the course. In B. L. Wadhera v. Union of India, the Court dealt with the failure of the Delhi municipal bodies to collect and dispose of the capital’s waste and directed the statutory authorities to perform the duties their own Acts imposed. In the same year Almitra H. Patel filed a writ petition under Article 32, Writ Petition No. 888 of 1996, asking the Court to intervene in the collection, storage, transportation, treatment and disposal of municipal solid waste across the country’s cities, on the ground that the failure to manage garbage was a threat to health and to the right to life. The petition named the problem at national scale: cities generated waste in quantities no administration was measuring honestly, collected it partially, and dumped it on open land at the urban edge, along roads, in wetlands and in water bodies, taking no endpoint responsibility for what happened to it.

The Court’s response was to appoint an expert committee, chaired by Asim Burman, which reported at the start of 1998 on the state of municipal solid waste in the Class I cities and on what a national regime would require. The committee’s work fed a draft set of rules in 1999, and the draft became the Municipal Solid Wastes (Management and Handling) Rules, 2000, made by the Union under the Environment (Protection) Act and notified in 2000. The choice of instrument is the founding fact of the modern law. A committee appointed by the Supreme Court, reporting on a State subject, produced rules made by the Union executive under an environmental statute, because that was the only legislative vehicle available that could reach every municipality in the country at once. Parliament did not debate a sanitation bill. No sanitation bill existed. The rulebook is a child of litigation, and it carries the marks of that parentage: it is written as a set of directions to authorities, with compliance schedules and reporting duties, because directions to authorities are what a court-driven process generates.

The 2000 Rules set a compliance calendar. Municipal authorities were to improve existing landfill sites, identify sites for future landfills, and set up waste processing and disposal facilities, with the system of collection, segregation, storage, transportation, processing and disposal to be in place against deadlines running to the end of 2003. The Supreme Court continued to monitor, and its orders of 2000, 2004, 2007 and 2010 record a rhythm that will be familiar to any reader of Indian environmental litigation: directions issued, compliance reported in part, deadlines extended, fresh directions issued. The Rules of 2000 had structural limits that monitoring could not cure. They applied within municipal areas and left the growing urban fringe, the census towns and the notified areas outside the frame. They placed their duties almost entirely on municipal authorities and said little to the waste generator, so segregation at source, the single practice on which all downstream processing depends, remained an exhortation rather than a duty owed by the household. They contemplated disposal more than processing, and they made no serious attempt to draw the informal workforce of waste pickers, who in fact recovered a large share of the recyclable material in every city, into the formal system.

By order dated 2 September 2014 the Supreme Court transferred the Almitra Patel proceedings to the National Green Tribunal, and the litigation entered its second institutional life, which the enforcement discussion below takes up. The transfer matters for the shape of the law: supervision of waste management passed from a constitutional court, which had generated the rules, to a specialist tribunal armed with statutory powers of compensation and restitution, which would go on to price the failure to comply. The rules themselves were replaced in 2016, and it is to the parent statute under which both sets of rules were made that the account turns next, because the character of the parent explains the character of everything made under it.

What the 2000 Rules built, and why they were replaced

Understanding the replacement requires a clear picture of what the Municipal Solid Wastes (Management and Handling) Rules, 2000 actually constructed, because much of their skeleton survives inside the 2016 design and the failure of the first rulebook is the best guide to the intentions of the second. The 2000 Rules applied to every municipal authority, a term they defined by reference to the municipal bodies responsible under State law for the management of municipal solid waste, and they made that authority answerable for the whole chain within its area: collection, segregation, storage, transportation, processing and disposal. They worked through schedules. One schedule set the compliance calendar already described, with landfill improvement, site identification and facility construction staged against dates running to the end of 2003. Another prescribed the specifications for landfill sites, their identification, the care to be taken in operation and the criteria for closure and post-closure monitoring. Others laid down standards: for compost quality, for the treatment of leachate, for ambient air and water quality around facilities. A management chain was prescribed in which the municipal authority reported to the district administration and the State board, and the State board reported annually to the Central Board, which reported to the Union government. The reporting pyramid of the 2016 Rules is this pyramid, retained.

Three features of the 2000 design deserve to be marked, because each explains a corresponding choice in 2016. The first is that the duty-bearer was singular. The municipal authority owed nearly every duty in the book, and the waste generator owed almost none beyond a general obligation not to litter and to cooperate with the authority’s system. The generator duties of 2016, the three streams, the fee, the bulk generator provisions, are the correction of that imbalance, made after sixteen years in which municipalities were blamed for failing to segregate waste that arrived at their gates irretrievably mixed. The second feature is the orientation towards disposal. The 2000 Rules were written when the policy problem presented itself as the absence of engineered landfills, and their centre of gravity sits in the landfill schedules: how to site one, line one, operate one and close one. Processing appears, but as an adjunct. By 2016 the centre of gravity had shifted to processing and recovery, with the landfill demoted to a destination for residues, and the shift records a change in the governing idea, from burying the problem safely to preventing most of the material from needing burial at all. The third feature is the silence about people. The 2000 Rules do not define a waste picker, do not mention the informal sector and make no provision for recognition or integration, although the informal recovery system was, throughout their life, the largest functioning recycling apparatus in the country. The 2016 Rules’ workforce provisions are a direct repudiation of that silence.

Why did the first rulebook fail on its own terms? The compliance calendar ran out at the end of 2003 with the great majority of cities in breach, and the Supreme Court’s monitoring orders over the following decade record facilities unbuilt, landfills unimproved and sites unidentified across most States. Part of the explanation is the one that runs through this article: the rules demanded capital works from bodies with no capital, and neither the rules nor the Court’s orders could appropriate the money. Part is administrative: the reporting pyramid transmitted returns that nobody at the receiving end had the staff to verify, so compliance became a paper condition. And part is that the 2000 Rules asked for the hardest thing first. An engineered landfill is the most capital-intensive, land-hungry and politically contested element of the system, since every neighbourhood resists hosting one, and the rules made it the centrepiece while leaving the cheap, distributed practices, segregation, composting, recovery, comparatively undeveloped. The 2016 redesign inverts the sequence: behaviour and recovery first, processing next, and the smallest possible residue to the landfill at the end. Whether the inversion has been given the means to succeed is the question the enforcement record answers, but as a reading of the earlier failure, the redesign is intelligent, and it was made by the same rule-making route, under the same parent Act, without Parliament being troubled at any point. The whole learning curve of Indian waste law, from the Burman Committee to the certificate markets of the plastic rules, has been travelled inside subordinate legislation.

The parent statute: what the Environment (Protection) Act supplies

The Environment (Protection) Act, 1986 is an umbrella statute. It was enacted by Parliament in the wake of the Bhopal disaster, drawing its legislative competence from Article 253 of the Constitution, which empowers Parliament to make law for implementing international agreements, and its preamble recites the decisions taken at the United Nations Conference on the Human Environment held at Stockholm in 1972. It does not, in the main, regulate anything directly. Its operative clauses confer powers: the power of the Central Government to take all such measures as it deems necessary or expedient for protecting and improving the quality of the environment, the power to make rules on the subjects the Act lists, and the power to issue directions, extending to the closure of an industry or the stoppage of a public utility. The detailed law of each pollution field, air, water in its residuary aspects, hazardous substances, noise, and waste in all its streams, is made by rules under the umbrella, and the Solid Waste Management Rules are one product of that design, made in exercise of the powers conferred by sections 3, 6 and 25 of the Act, as their own preamble records. The rule-making architecture, the direction power and the penalty scheme of the parent Act are treated in the series account of the Environment (Protection) Act 1986 and its rule-making design, and this article takes that structure as given and asks what it means for waste.

Three consequences flow from the choice of an umbrella environmental statute as the vehicle for sanitation law, and each of them runs through the rest of the subject. The first is jurisdictional. A rule made under the Environment (Protection) Act binds because the Act says rules bind; it can impose duties on any person, including a municipality, and disobedience is an offence against the parent Act. That is how a Union instrument reaches a State subject without a constitutional amendment and without the States’ consent: it does not legislate on sanitation as such, it legislates on the environment, and municipal waste is reached as an environmental matter. The reasoning is constitutionally available and has never been struck down, but it has a price. The rulebook must always present itself as environmental protection, and its instruments are the instruments of environmental regulation: authorisations, standards, monitoring by pollution control boards, and prosecution or penalty under the parent Act. A service that residents experience as a municipal service is regulated as if it were an industrial emission.

The second consequence is financial, and it is the deeper one. Subordinate legislation cannot appropriate money, cannot create a tax, and cannot endow an institution with a revenue of its own. A statute could have created a sanitation fund, assigned a share of a tax, or imposed a duty on State governments to devolve specified resources to municipalities for waste functions. Rules can do none of these things. They can direct a local body to make adequate provision of funds in its annual budget, and the 2016 Rules do exactly that, in terms that require waste expenditure to be provided for before money is allocated to discretionary functions. But a direction to budget is not a budget. The local body’s actual resources continue to be whatever its State Act, its tax base and State and Union transfers make them. The instrument that creates the duty is therefore structurally incapable of creating the means, and every enforcement failure in this field has to be read against that incapacity before it is read as unwillingness.

The third consequence is about enforcement identity. Environmental statutes are policed by environmental regulators. The State pollution control boards, constituted under the water and air statutes, are the authorising and monitoring authorities for waste facilities, and the Central Pollution Control Board coordinates standards and reporting at the national level. These boards were designed to consent and prosecute industries. In the waste field they find themselves supervising municipalities, which are not industries but elected governments of another tier, delivering a daily public service. The fit is awkward in both directions. The boards have no leverage over a municipality’s establishment, budget or elections, and the municipality has no seat in the boards’ governance. When supervision by the boards has proved insufficient, the system’s recourse has been to the tribunal, and the result is the feature the brief for this article identifies as central: a municipality’s principal accountability for its garbage runs to an environmental tribunal rather than to its residents or to the State department that funds it. That accountability structure, in which the enforcing authority neither elects nor finances nor is elected by the body it enforces against, is not an accident of administration. It is the predictable output of regulating a municipal service through an environmental statute. Three further provisions of the parent Act shape how the rulebooks sit against the rest of Indian law, and a practitioner needs them. Section 24 gives the Act and its rules overriding effect against inconsistent enactments, with a single exception: where an act or omission is punishable both under this Act and under another law, the offender is punished under the other law and not under this one. The override explains why a State municipal Act or a set of bye-laws cannot lawfully dilute a rulebook obligation, and the exception explains why prosecutions for the same conduct are sometimes found in the criminal register rather than the environmental one. Section 22 bars civil courts from entertaining suits in respect of anything done under the Act, channelling challenge towards the appellate and tribunal routes and, after the Jan Vishwas recast, towards the National Green Tribunal for penalties. Section 23 permits the Union government to delegate its powers under the Act to officers and authorities, which is the provision under which much of the day to day administration by boards and designated officers proceeds. Read together, the three sections describe an Act designed to be administratively self-contained: its rules override, its forum is specialised, and its executive reach is delegated. That design is part of why the system could be built without the States’ legislative cooperation, and equally part of why it sits awkwardly against municipal institutions whose own statutes were never amended to receive it.

The Solid Waste Management Rules, 2016: coverage and design

The Solid Waste Management Rules, 2016 were published on 8 April 2016. Their preamble records that a draft had been published for objections and suggestions in June 2015, and that they are made under sections 3, 6 and 25 of the Environment (Protection) Act in supersession of the Municipal Solid Wastes (Management and Handling) Rules, 2000, except as respects things done or omitted before the supersession. The supersession is the first thing to fix. The 2016 Rules are not an amendment of the 2000 Rules; they are a replacement rulebook, and the differences between the two are the measure of what sixteen years of supervision had taught.

Which places do the 2016 Rules reach that the 2000 Rules did not?

The 2016 Rules apply to every urban local body and beyond it: to outgrowths in urban agglomerations, census towns, notified areas, industrial townships, railways, airports, airbases, ports, defence establishments, special economic zones, government organisations and notified places of pilgrimage, and to every generator in those areas.

The extension of coverage is the design decision from which the rest follows. Urban India does not end at the municipal limit. The census town, urban in its economy and density but governed by a panchayat, the industrial township run by a public sector undertaking, the railway colony, the cantonment-like defence establishment, the pilgrimage town whose floating population multiplies its resident count on festival days: each of these generated municipal-type waste in quantity while standing outside the municipal rulebook. The 2016 Rules chase the waste rather than the institution, applying wherever the listed areas and generators are found. The carve-out is equally deliberate. Industrial waste, hazardous waste, bio-medical waste, e-waste, lead acid batteries and radioactive waste are excluded from the definition of the field these rules govern, because each is the subject of its own rulebook under the same parent Act, and the parallel sets are examined below. What remains, the solid waste of households, commerce, institutions, streets, markets, gardens and drains, is the subject here.

The coverage list also settles the position of institutions that run their own territories. A railway station, an airport, a port, a defence establishment or a special economic zone inside a city’s geography generates waste of exactly the municipal kind, and the rules apply to the area notwithstanding that no municipality governs it. The institutional occupier must work the system the local authority operates, handing segregated waste into collection and paying the charges the framework sets, or build equivalent arrangements within its own administration under the same duties. The design is worth noting because it reverses the usual federal courtesy under which enclaves administer themselves; for the purposes of waste, the enclave is treated as part of the urban fabric its waste enters. The same logic reaches the notified pilgrimage and religious places, whose administrations must plan for festival peaks that can exceed the resident population’s generation many times over, and whose failure modes, the riverbank after a festival, are among the most photographed in Indian environmental reporting.

The definitions in Rule 3 do quiet but decisive work, and four of them carry the regime. A bulk waste generator is defined by a list of institutional occupants, government departments and undertakings, local bodies, hospitals and nursing homes, schools, colleges and universities, hostels, hotels, commercial establishments, markets, places of worship, stadia and sports complexes, qualified by an average waste generation rate exceeding one hundred kilograms per day; the category matters because the rules cast heavier, premises-level duties on those who generate at that scale. A material recovery facility is defined as the place where non-compostable waste is temporarily stored so that segregation, sorting and recovery of recyclables can be performed by authorised waste pickers, informal recyclers or other workers engaged for the purpose; the definition writes the informal workforce into the facility’s own description. Sanitary land filling is defined as the final and safe disposal of residual waste and inerts on land, in a facility designed with protective measures against pollution of ground water, surface water and air; the definition matters because it denies the name of sanitary landfill to the open dump, which the rules define separately as land used for disposal without following the principles of sanitary land filling. And residual solid waste is defined as the waste and rejects from processing facilities not suitable for recycling or further processing, which fixes the landfill’s lawful diet: what processing cannot use, and nothing else.

The architecture of the rules as a whole is a chain of duties running from the Centre to the household. The Ministry of Environment, Forest and Climate Change bears overall responsibility for implementation review and maintains a central monitoring committee. The Union urban affairs ministry, the Ministry of Housing and Urban Affairs in its present name, must formulate a national policy and strategy on solid waste management, promote research, and build the capacity of local bodies. The fertiliser, agriculture, power and renewable energy ministries carry small, specific duties at the edges: market development assistance for city compost and its co-marketing with chemical fertiliser, flexibility in the Fertiliser Control Order for compost, tariff decisions and compulsory purchase for waste to energy power, and subsidies for waste to energy plants. The Secretary in charge of urban development in each State must prepare the State policy and strategy within one year, ensure land is identified and allocated for processing and disposal facilities, and see master plans reserve space for them. The District Magistrate reviews the performance of local bodies in the district at least once a quarter. The Central Pollution Control Board sets environmental standards for facilities, coordinates the State boards and consolidates the annual reporting. The State pollution control boards authorise facilities and enforce the rules through the local bodies. And at the end of the chain stand the two actors on whom the physical work depends: the local authority, with the longest duty list in the rules, and the waste generator, with the shortest and the most widely evaded. Those two duty sets are the operative core of the regime, and each gets its own treatment.

The duties of the waste generator

Rule 4 states the duties of every waste generator, and its first clause contains the practice on which the entire regime depends. Every waste generator shall segregate and store the waste generated in three separate streams, namely biodegradable waste, non-biodegradable waste and domestic hazardous waste, in suitable bins, and hand over the segregated waste to authorised waste pickers or waste collectors as directed or notified by the local authority. The three streams correspond to three different destinies. Biodegradable waste, the wet fraction of food and garden matter, is destined for composting or bio-methanation. Non-biodegradable waste, the dry fraction of paper, plastic, metal, glass and textile, is destined for recovery and recycling, with a combustible residue destined for energy recovery. Domestic hazardous waste, the discarded paint drums, pesticide cans, fluorescent bulbs, expired medicines, broken mercury thermometers, used batteries, needles and contaminated gauze of household life, is destined for the hazardous waste stream and must never enter either of the others. Segregation at source is the act that makes each destiny possible, and mixing at source is the act that defeats all three, because a compost plant cannot compost plastic, a recycler cannot recover value from material soaked in food waste, and a hazardous item in the general stream endangers every hand that touches the stream thereafter.

The remaining clauses of Rule 4 refine the duty at its edges. Used sanitary waste, diapers and sanitary pads, must be wrapped securely in the pouches provided by the manufacturers or brand owners of those products, or in suitable wrapping, and placed in the bin for dry waste. Construction and demolition waste must be stored separately on the generator’s own premises and disposed of under the Construction and Demolition Waste Management Rules, 2016. Horticulture and garden waste must likewise be stored separately on the premises and disposed of as the local body directs. No waste generator shall throw, burn or bury solid waste on streets, in open public spaces outside the premises, or in drains or water bodies; the prohibition is unqualified and is the clause most often breached in the country on any given day. The organiser of an event or gathering of more than one hundred persons at an unlicensed place must intimate the local body at least three working days in advance and must ensure segregation and handover at the event. Street vendors must keep suitable containers for the waste they generate and deposit it at the depot, vehicle or container the local body specifies. Resident welfare associations, market associations, gated communities and institutions with an area above five thousand square metres, and hotels and restaurants, must, in partnership with the local body, ensure segregation and sorting and are expected to process their biodegradable waste within their premises as far as possible; bulk generators as defined carry the same premises-level responsibility at institutional scale. The pattern across these clauses is consistent: the closer the generator is to commercial scale, the more the rule expects the generator to internalise the processing, and the household is asked for the one act only it can perform, which is to keep the streams apart.

Rule 4 then attaches the money. All waste generators shall pay such user fee for solid waste management as is specified in the bye-laws of the local body. The rules do not set the fee. They cannot, because a fee for a municipal service is a creature of municipal law, and the amount, the incidence and the collection machinery are left to each local body’s bye-laws. The generator is also exposed to a spot fine for littering and for non-segregation, and here too the operative figure is local: the rules define a fine as a penalty imposed under the bye-laws, and they require the local authority, as part of its own duties, to frame the criteria for levying spot fines and to delegate the power to levy them. The legal position is therefore precise and widely misunderstood. Segregation is a duty under central rules. The user fee is a duty under central rules payable at a locally fixed rate. The fine for failing either is a creature of local bye-law, exists in figures that vary from city to city, and in most cities is levied rarely or never, because levying it requires an authorised officer, a receipt machinery, and a willingness to fine the residents on whom the municipality’s elected leadership depends. A duty whose sanction sleeps is not a nullity; it changes what the local body may lawfully demand and what a court or tribunal may treat as the standard of conduct. But the reader should understand the household fine as the brief for this article directs: a provision that exists on paper almost everywhere and is levied almost nowhere.

Who fixes the user fee a household pays for waste collection?

The local body fixes it, in its bye-laws. The central rules command that a user fee be paid and require the local authority to prescribe the fee from time to time and collect it directly or through an authorised agency, but the amount is municipal business, set under the State municipal Act, and it differs from city to city.

One further feature of the generator duties deserves emphasis, because it explains why compliance is a collective problem rather than a merely individual one. Segregation is only worth performing if the collection system preserves it. A household that separates three streams and watches the collector empty all three into a single compartment has been taught, by the system’s own conduct, that the duty is theatre. The rules understand this, and the local authority duties examined next include the transport of segregated streams in compartmentalised and covered vehicles to their respective facilities. The generator’s duty and the authority’s duty are two halves of one covenant, and the enforcement record of each half cannot be judged without the other. Where collection is unreliable, household compliance collapses for reasons that are rational, and any honest account of the regime must record that the duty without the service changes behaviour only at the margin. Two further duty sets in the rules fall on producers rather than on households or municipalities, and they complete the generator picture. All manufacturers of disposable products such as tin, glass and plastic packaging, and brand owners who introduce such products into the market, must provide necessary financial assistance to local authorities for the establishment of waste management systems, and brand owners who sell or market products in non-biodegradable packaging must put in place a system to collect back the packaging waste their products generate. Manufacturers, brand owners and marketing companies of sanitary napkins and diapers must explore the use of recyclable materials in their products or provide a pouch or wrapper for the disposal of each unit along with the packet, and must educate the public on the wrapping and disposal of their products. These duties are the solid waste rules’ own, home-grown version of producer responsibility, older and softer than the quantified certificate regime the plastic rules later built, and they matter here because they show the 2016 drafters already reaching, inside the municipal rulebook itself, for the principle that the cost of a product’s end of life should travel back up the chain to the enterprise that designed the product. The special territory of the hills should also be recorded. For hilly areas the local authority’s duties are those of Rule 15 with additions: the construction of a landfill on the hill is to be avoided, a transfer station at a suitable enclosed location receives the residual and inert waste, land in the plains within twenty-five kilometres is to be identified for the sanitary landfill, failing which a regional landfill is to be attempted; bye-laws must prohibit littering by citizens and speak directly to tourists, who are to be told of the regime at the town’s entry point and through hotels and hoardings, and the local body may levy a solid waste management charge on the tourist at entry to make the service sustainable. The hill provisions are a small essay in the rules’ realism: they recognise that terrain defeats the standard template, that the floating population is the waste problem of a hill town, and that the visitor who generates the waste can be charged for it at the gate.

The duties of the local authority

Rule 15 casts on local authorities, and on the village panchayats of census towns and urban agglomerations, the longest list of duties in the rulebook, running from clause (a) to clause (zg) and beyond, and it is best understood in groups. The planning group comes first. The local authority must prepare a solid waste management plan in accordance with the State policy and strategy, within six months from the notification of that policy, and must frame bye-laws incorporating the provisions of the rules within one year from their notification. The State policy itself is due within one year under the duties of the Secretary in charge of urban development, so the calendar is nested: national rules, then State policy, then the local plan and the local bye-laws that make the rules enforceable against the resident. A failure at the top of the nest delays everything beneath it, and the annual reporting of the Central Pollution Control Board has repeatedly recorded States and local bodies running years behind this opening sequence.

The collection group is the visible service. The authority must arrange door to door collection of segregated waste from all households, expressly including slums and informal settlements, and from commercial, institutional and other non-residential premises, collecting from the entry gate or a designated point in multi-storey buildings, malls and housing complexes. It must collect market waste daily and promote decentralised composting or bio-methanation at or near markets; collect street sweepings and drain silt separately on a daily, alternate-day or twice-weekly rhythm matched to density and activity; keep horticulture waste apart and process it in parks and gardens as far as possible; and transport each segregated stream, in compartmentalised and covered vehicles, to its proper destination, the biodegradable fraction to composting or bio-methanation, the dry fraction to material recovery or processing, and construction and demolition waste under the rules made for it. The authority must also establish waste deposition centres for domestic hazardous waste, one for every twenty square kilometres or part of it, notify their timings, and ensure the safe storage and onward transport of what is deposited to the hazardous waste facility or as the State board directs. The system the rules describe is thus a logistics network with a legal personality: segregated intake, separated transport, and distinct destinations, and its absence in a given city is measurable at every joint.

The workforce group is where the 2016 Rules break most sharply with their predecessor. The authority must establish a system to recognise organisations of waste pickers and informal waste collectors, and promote and establish a system for their integration into solid waste management, including door to door collection. It must facilitate the formation of self help groups, provide identity cards, and thereafter encourage integration. It must set up material recovery facilities or secondary storage facilities with sufficient space for sorting, and provide easy access to waste pickers and recyclers for the collection of segregated recyclables such as paper, plastic, metal, glass and textile from the source or from the facilities, with storage bins coloured green for biodegradable waste, blue for recyclable waste and black for other waste. It must provide training in solid waste management to waste pickers and waste collectors, and must ensure that the operator of a facility provides personal protection equipment, uniforms, fluorescent jackets, gloves, raincoats, footwear and masks, to all workers handling solid waste, and that the equipment is used. The significance of this group is easy to miss if the rules are read as an environmental instrument alone. Read as labour-adjacent law, the 2016 Rules are the first national instrument to treat the waste picker as a participant to be recognised, organised, identified, trained and equipped, rather than as a trespasser on the municipal system. The implementation of that recognition is uneven, and the position of the workforce is examined in its own section below, but the textual commitment is unambiguous.

The processing and disposal group converts collection into treatment. The authority must facilitate the construction, operation and maintenance of processing facilities, on its own or with private participation, preferring decentralised processing, and adopting the listed technologies: bio-methanation, microbial composting, vermi-composting and anaerobic digestion for the biodegradable fraction, and waste to energy processes including refuse derived fuel for the combustible fraction, supplied as feedstock to power plants or cement kilns. It must undertake the construction, operation and maintenance of sanitary landfills and associated infrastructure in accordance with Schedule I, for the disposal of residual waste. Two clauses fix the landfill’s shrinking role. The authority must stop landfilling or dumping mixed waste once the timeline for setting up and operationalising sanitary landfills has run, and it must allow only non-usable, non-recyclable, non-biodegradable, non-combustible and non-reactive inert waste, together with pre-processing rejects and residues from processing facilities, to go to sanitary landfill, with every effort made to recycle or reuse the rejects towards the objective of zero waste going to landfill. For the inheritance of the past, the authority must investigate and analyse all old open dumpsites and existing operational dumpsites for their potential for biomining and bio-remediation, and where feasible bio-mine or bio-remediate them; where that potential is absent, the dumpsite must be scientifically capped in accordance with landfill capping norms to prevent further damage to the environment.

Where does a municipality’s waste authorisation come from?

From the State pollution control board. A local body whose waste exceeds five tonnes a day must apply for authorisation to set up a processing, treatment or disposal facility, the board must examine the proposal against the views of other agencies and issue the authorisation within sixty days, and the authorisation runs in step with the facility’s consents.

The administrative group closes the list. The authority must make adequate provision of funds for capital investment and for operation and maintenance of solid waste management services in its annual budget, ensuring that funds for discretionary functions are allocated only after the requirement for waste services and other obligatory functions is met, a clause whose logic is Ratlam translated into a budgeting rule. It must obtain the board’s authorisation for its facilities and renew it, applying at least sixty days before expiry. It must submit its annual report by the thirtieth of April to the municipal administration, which forwards it to the State urban development department and to the State board, feeding the reporting chain described in the enforcement section. It must frame the criteria for spot fines and delegate the levying power. And it must create public awareness through information, education and communication campaigns, teaching the generators the content of their own duties, from segregation and home composting to the payment of the monthly user fee on which the sustainability of the service is said to depend.

A timeframe rule, Rule 22, attaches dates to the physical build-out. Sites for processing facilities and for common regional sanitary landfills were to be identified within one year of notification, and procured within two. Segregation at source was to be enforced, and door to door collection of segregated waste in covered vehicles ensured, within two years. Processing facilities were to be set up within two years by local bodies of one lakh population or more, and within three years by smaller bodies and census towns. Sanitary landfills, common, regional or stand alone, for the disposal of permitted residual waste only, were to be set up within three years. Bio-remediation or capping of old and abandoned dumpsites was allowed five years. The calendar was demanding when it was written and it has not been met at national scale, which is the finding the Central Pollution Control Board’s annual reports and the Tribunal’s proceedings converge on. The rules’ answer to the missed calendar is not a fresh calendar but escalation: reporting, review by the district and State machinery, and, at the top of the ladder, the tribunal’s compensation jurisdiction, to which the account turns by way of the constitutional setting that makes the whole structure necessary.

Standards at the end of the chain: landfill specifications, buffer zones and the energy route

The duties described so far are duties of conduct: segregate, collect, transport, process. The rules also prescribe duties of specification, the physical standards a facility must meet, and these live in the two Schedules. Schedule I sets the specifications for sanitary landfills, beginning with site selection. The land-assigning department of the State must provide and notify suitable sites. A landfill is to be planned, designed and developed with documentation of its construction plan and a closure plan in phased form; it is to be sited to make use of nearby processing facilities, or the processing facility is to be planned as an integral part of the landfill site; it is to be large enough to last for at least twenty to twenty-five years and developed in cells in phases, to avoid water logging and misuse; and it must stand at prescribed distances from sensitive receptors, one hundred metres from a river, two hundred metres from a pond, and two hundred metres from highways, habitations, public parks and water supply wells. Existing landfill sites in use for more than five years are to be improved in accordance with the Schedule. Schedule II carries the operating standards: the specifications compost must meet before it may be marketed as city compost, the parameters for leachate and for ground water, ambient air and noise around processing and disposal facilities, and the standards for incineration and refuse derived fuel where those routes are used. The State boards monitor adherence to both Schedules, and the Central Board formulates and updates the environmental standards themselves. The point of recording the Schedules in a legal article is that they convert the question whether a dump is lawful into a question of measurement. A facility either stands the prescribed distance from the river or it does not; its leachate either meets the parameters or it does not; and it is this measurability that allows a tribunal, years later, to move from exhortation to computation when it prices a default.

Around every processing and disposal facility above five tonnes a day, the rules require a buffer zone, a zone of no development maintained within the allotted area, with the State urban development secretary notifying buffer zones in consultation with the State board and the Central Board publishing guidelines for the restriction of residential, commercial and other construction activity beyond the facility’s boundary by size of facility. The buffer zone is a small provision with a large grievance inside it. Facilities are sited, lawfully and after search, at the urban edge; the city then grows around them; the residents who arrive later experience the facility as an imposition and litigate for its closure, while the facility’s operators answer that the buffer the law required was consumed by the development the law forbade and other authorities permitted. Many of the closure battles in the Tribunal’s waste docket are buffer zone battles in substance, and they illustrate a recurring property of this field: the rule can be perfectly complied with at the moment of siting and defeated thereafter by decisions taken in other legal registers, in planning permissions and land use conversions that the waste rulebook does not govern.

The energy route has its own criteria. Non-recyclable waste with a calorific value of fifteen hundred kilocalories per kilogram or more shall not be disposed of in landfills; it must be used for generating energy, or converted into refuse derived fuel, or given away as feedstock for preparing such fuel, and high calorific waste is to be used for co-processing in cement or thermal power plants. A waste to energy plant above five tonnes a day requires the State board’s authorisation, which the board is to decide within sixty days. Industrial units using fuel within one hundred kilometres of a refuse derived fuel plant were required, within six months of the rules’ notification, to arrange to replace at least five per cent of their fuel requirement with refuse derived fuel so produced. These provisions make the rules’ hierarchy operational: recovery of material first, recovery of energy from what cannot be recovered as material, and land reserved for the inert remainder. They also expose the hierarchy’s practical fragility, because the calorific value of Indian municipal waste, wet with its high biodegradable fraction, sits low when segregation fails, so the energy route depends on the same source separation as every other route. A city that mixes its waste produces a stream too wet to burn well and too contaminated to compost, and discovers that the elegant hierarchy of the rulebook is, in operation, a single point of failure located in the household’s kitchen.

One consignment of waste, followed through the rules

The regime is easier to judge when its paper chain is laid over a physical one, so consider a single morning’s waste from a single residential street, and follow it through the duties the rules attach to each hand it passes through. The waste begins in kitchens, where Rule 4 requires it to be sorted into three streams before it leaves the house: the wet fraction of peels, leftovers and garden matter; the dry fraction of paper, plastic, metal and glass; and the small but dangerous domestic hazardous fraction of bulbs, batteries, expired medicines and paint tins. Sanitary waste travels wrapped, inside the dry stream. The first legal event is therefore a private act performed without witnesses, and the whole system is built on its being performed honestly by millions of people who will never read the rule that requires it.

The second event is the collection round. The local authority’s duty is door to door collection of the segregated streams, from the doorstep or, in a housing complex, from the entry gate. The collector, who may be a municipal worker, a contractor’s worker, or an authorised waste picker integrated into the round under the recognition system, receives the streams separately; the rules require the streams to be transported unmixed, in compartmentalised and covered vehicles, and they require the workers on the round to have been educated for segregated collection and the facility operator to have equipped them with protective gear. Where the round collects mixed waste into one compartment, the legal failure is the authority’s and not the household’s, and the household’s incentive to segregate dies at that moment for reasons any court would recognise as rational.

The third event is the material recovery facility, where the dry stream is sorted into its saleable fractions: paper grades, plastic grades, metal, glass, textile. The sorting is performed, by the definition of the facility itself, with the participation of authorised waste pickers and informal recyclers, whose access the local authority must facilitate; the fractions leave as commodities into the recycling economy, the kabadi chain of buyers and aggregators that long predates the rules and that the rules absorb rather than replace. The wet stream travels separately to its own destination: a compost plant, a bio-methanation plant producing biogas and slurry, a market-side decentralised unit if the waste is market waste, or, for the housing complex that qualifies, a composting arrangement within its own premises. What emerges as compliant city compost must meet the standards of Schedule II, and the fertiliser department’s machinery of market development assistance and co-marketing with chemical fertiliser exists to give that compost a route to farms.

The fourth event disposes of what neither sorting nor processing could use. The combustible residue may go as refuse derived fuel to a cement kiln or a waste to energy plant, under the calorific discipline described in the standards section. The domestic hazardous fraction goes from the deposition centre, one for every twenty square kilometres, to the hazardous waste treatment, storage and disposal facility under the hazardous rules. The inert remainder, street sweepings and silt, processing rejects and stabilised residues, goes at last to the sanitary landfill, into a cell built and lined under Schedule I, on a site notified by the State, authorised by the board, buffered against the neighbourhood, and designed to close in phases across a life of twenty to twenty-five years. Every stage of that journey is somebody’s legal duty, and the consignment’s paperwork, the facility’s annual report, the local body’s annual report, the board’s consolidated report, ascends the reporting pyramid behind it. Set beside this chain the waste of the same street in a city where the system exists only in the returns: mixed at the kitchen because the round mixes, dumped at the transfer point because the facility was never built, burned at the dumpsite edge because burning is the cheapest volume reduction available, and rained on through the monsoon into the drain. The difference between the two cities is not the law, which is identical in both. It is land allotted or withheld, a facility authorised or stalled, a budget line honoured or raided, and an administration that treats the rulebook as an operating manual or as a reporting obligation. The law of waste in India is uniform. Its administration is local, and that is the deepest sense in which sanitation remains a State subject whatever the rulebook’s source.

The view from the municipal commissioner’s desk

The rules read differently from the chair that must execute them, and a pillar treatment owes the reader that translation. A municipal commissioner inherits, on taking charge of a city, a bundle of dated obligations: a State policy that may or may not exist in usable form, a local plan the rules required within six months of it, bye-laws that may predate the rules and contradict them in their fee and fine schedules, an authorisation position for facilities that may include facilities never built, and an annual report that must be filed by the thirtieth of April whether or not the underlying system exists to be reported on. The commissioner’s first discovery is that the rules presume an asset base, sites, facilities, a fleet, a recovery centre, that the city may possess only in fragments, and that the timeframe of Rule 22 ran from a notification date years before the present incumbent’s arrival, so that the default the rules describe is, in most cities, the inherited condition rather than a fresh breach.

The operating decisions that follow are structured by three features of the design. The first is contracting. Few municipalities collect and process with their own establishment alone; collection routes, transport and processing are concessioned to private operators and agencies, and the rules anticipate this, defining the operator of a facility to include the local body and any entity it appoints, defining the tipping fee as the fee or support price the local authority or an authorised State agency pays the concessionaire for processing waste or disposing of residual waste at the landfill, and making the operator answerable for standards, protective equipment and annual reporting. The concession structure solves the establishment problem, since the contractor hires the crews the municipality cannot sanction posts for, and creates the accountability problem that runs through the sector: the duty remains the local body’s in law, while the performance sits with a contractor whose contract the residents cannot see and whose defaults the body must pursue through commercial remedies while answering for them before the board and the Tribunal. The second feature is the budget clause in operation. Rule 15 requires waste provision to be made before discretionary allocation, but the clause governs the ordering of a budget whose total is set elsewhere, by the State’s devolution, the city’s tax effort and the mission’s grants; a commissioner can honour the clause perfectly and still command a sum that buys collection without processing, or processing without the fleet to feed it. The third feature is the authorisation cycle. Facilities must be authorised, consents kept alive, renewals sought sixty days before expiry, and standards in the Schedules demonstrated to a board that inspects at its own rhythm; a plant that operates during a lapsed authorisation exposes the body even if its environmental performance is sound, so the paper discipline of the regime is a real discipline, consuming the scarcest resource in a municipal office, which is senior attention.

None of this is an argument against the rules. It is the reason their enforcement history takes the shape it does, in which the defaults that reach the Tribunal are disproportionately the defaults of the asset base, land not allotted, facilities not built, dumps not remediated, rather than of daily conduct. Daily conduct, the round not run, the stream mixed at the transfer point, appears in grievance registers and mission dashboards, and only rarely climbs the ladder to a compensation order. The commissioner’s desk is where the triangle of duty, money and sanction meets a fourth term the legal texts omit: sequence. Everything cannot be built first, and the order in which a city builds determines which duties it can honestly perform in the interval. The rules, written as simultaneous obligations, leave the sequencing to the administrator and the blame for the interval to the same desk.

The constitutional hook and the funding mismatch

The Constitution enters the subject at one precise point. The Seventy-fourth Amendment of 1992 inserted Part IXA on municipalities and added the Twelfth Schedule, listing the eighteen matters in respect of which a State legislature may endow municipalities with powers and authority. Item 6 of that Schedule reads: public health, sanitation conservancy and solid waste management. The entry is the constitutional hook on which the municipal waste function hangs, and its placement inside the pillar treatment of the 74th Amendment and urban local bodies shows the feature that decides its force: Article 243W, the provision that introduces the Schedule, is permissive. The State legislature may endow municipalities with such powers as may be necessary to enable them to function as institutions of self-government, including in relation to the Twelfth Schedule matters. The Constitution thus names the function and assigns its conferral to the discretion of those same State legislatures whose municipal Acts already carried sanitation as an obligatory duty. The Twelfth Schedule entry dignifies the function; it does not fund it, staff it or transfer a revenue source with it.

Set the three layers side by side and the structural mismatch stands out in full. The duty layer is Union-made: rules under an environmental statute prescribe, in fine detail, what the municipality must do, from the colour of its storage bins to the composition of what may enter its landfill. The institutional layer is State-made: the municipality’s functions, taxation, establishment, borrowing and supersession are governed by State municipal law, which the Union rules do not touch. The money layer is mixed and mostly elsewhere: municipal own revenue, State transfers, Finance Commission grants routed through States, and Union mission grants tied to programme outcomes. An instrument that can create an obligation cannot create the means to discharge it, and the local body is answerable to an environmental regulator for a service it is funded for by a State. This is the same mismatch between assigned function and controlled resource that the series records in the rural setting in the account of panchayat devolution in practice, with the urban difference that the urban body’s obligations are specified by a Union rulebook of unusual granularity and policed by a tribunal.

The newest layer of the money is the Finance Commission’s, and it deserves recording because it shows the fiscal system beginning to price the duty. The Fifteenth Finance Commission, whose recommendations cover the years from 2021 to 2026, made substantial grants to urban local bodies, routed through the States, and attached conditions of two kinds. Entry level conditions require the publication of audited accounts and the notification of property tax floor rates, disciplines aimed at the own-revenue weakness described above. For cities of a million or more, a portion of the grant is performance based, assessed against service level benchmarks that include air quality and the management of solid waste and sanitation, so that a city’s waste performance carries a fiscal price set in advance and paid for achievement rather than levied after default. The sums do not close the funding gap of the sector, and the conditions bind only at the margin of a municipal budget. But the direction is the one the verdict of this article identifies as the missing discipline: money arriving with the duty, through the same channel, against the same measures, instead of a rulebook in one ministry, a mission in another and a penalty in a tribunal, each ignorant of the other two.

The money that has actually moved the system arrived as a scheme. The Swachh Bharat Mission, Urban was launched on 2 October 2014 as a Union programme, administered by the urban affairs ministry, offering central assistance to States and local bodies for sanitation and solid waste projects against mission guidelines, city plans and reform conditions. Its second phase, Swachh Bharat Mission, Urban 2.0, was launched on 1 October 2021 for the five years from 2021 to 2026, with a total financial outlay of Rs 1,41,600 crore including committed central assistance of Rs 36,465 crore, against an outlay of Rs 62,009 crore for the first phase; its stated vision is garbage free cities, achieved through source segregation, door to door collection, scientific processing of all fractions of waste, safe disposal of residual waste in scientific landfills and remediation of all legacy dumpsites. The mission’s legal character is the point. It is not a statute, creates no rights and imposes no duties that a court can enforce as such; it is a funding and target framework, under which money flows to States against proposals and outcomes. But its practical weight exceeds that of the rulebook it supports, because it pays for the material recovery facilities, compost plants, bio-methanation plants, refuse derived fuel facilities and landfill works that Rule 15 commands and municipal budgets could not carry. The operative combination in Indian waste governance is therefore exactly the one the brief for this article isolates: central rules, central scheme money and State municipal law. The rules say what must happen. The mission pays for part of it. The State Act constitutes the body that must do it, and the State’s fiscal choices decide whether the body can.

The mismatch has a corollary that the enforcement record makes vivid. When a tribunal imposes environmental compensation on a State or a municipality for unprocessed waste, the compensation is paid out of public funds of the same order as the funds that would otherwise finance the service, into a ring-fenced account earmarked for restoration. The municipal objection to that arrangement is not frivolous, and it is given full voice in the section on the two cases below. For the structural account, the point is narrower: a system in which the sanction is a transfer within the public purse, from the service budget to a restoration account, has built its deterrence out of the same money whose scarcity caused the default. That circularity is not a drafting error anyone can redraft away inside a rulebook. It is what enforcement looks like when the duty-bearer is a public body and the duty was created by an instrument without a purse.

State variation and the cities that made the template work

A uniform rulebook laid over State institutions produces, predictably, a varied map, and the variation is instructive because it separates what the rules can do from what only administration can. The State policy and strategy that each State had to prepare within a year differs in ambition and in the machinery it creates: some States built mission directorates and professional support units for their municipalities, others lodged the subject in the municipal administration directorate with its existing staff. Bye-laws, the instrument that binds the resident, vary in their fee levels, their fine levels and their enforcement machinery by orders of magnitude between cities. The State municipal Acts beneath everything differ in the obligatory functions they list, in the taxes they assign and in the State government’s powers over the local body. A researcher comparing two cities is therefore never comparing two implementations of one system; the comparison is between two systems that share a rulebook, a mission and a tribunal, and differ in almost everything else.

The standing demonstration that the template can be made to work is Indore in Madhya Pradesh, which has placed first in the Swachh Survekshan, the mission’s annual ranking of cities, repeatedly and by wide margins, and whose municipal corporation built its system on exactly the elements the rules prescribe: door to door collection of waste segregated into multiple streams at source, a fleet organised around the streams, processing of the wet fraction, recovery of the dry fraction through organised sorting, and the conversion of its legacy dumpsite through bio-mining into recovered land. Indore’s significance for a legal account is not civic pride. It is that the city’s methods required no legal innovation whatsoever. Every element sits within the four corners of the 2016 Rules and a municipal budget; what the city added was administrative continuity, political protection for enforcement against its own residents, and the willingness to levy and collect the charges the bye-laws everywhere authorise and almost nowhere collect. Kerala’s decentralised experience makes the complementary point from the other end of the design spectrum: through the Suchitwa Mission, the State’s nodal agency for sanitation, Kerala pushed processing downwards to the household and the ward, with home composting, community facilities and material collection run substantially through women’s self help networks, reducing the tonnage that ever reaches a municipal facility and with it the capital the system needs. The two models disagree about scale and agree about the variable that matters, which is the organisation of people rather than the text of rules. For the argument of this article the lesson is exact: where the system works, it works inside the existing legal architecture, which proves the architecture is not unusable; and the places where it does not work are not, in the main, places where a different rulebook would have saved it, which proves the architecture is not the binding constraint. The binding constraints are land, money, administrative continuity and the political cost of charging residents, and a sanitation statute, to repeat the test applied below, is worth having only if it moves one of those four.

The parallel rule sets: one parent, six rulebooks

Rule 2 of the Solid Waste Management Rules excludes from their field the waste streams governed by separate rules, and the exclusions map the rest of the family. Each of the following rulebooks is made under the Environment (Protection) Act, each assigns duties to producers, occupiers, operators and authorities in the pattern the parent makes possible, and a reader who understands one understands the grammar of all. Researchers assembling the family for comparison can keep the waste rulebooks together in a single office file viewer while working through the duties each one casts, because the contrasts between them are where the design choices show.

Plastic waste is governed by the Plastic Waste Management Rules, 2016, notified in March of that year, which replaced the earlier plastic waste rules of 2011. Their distinctive contribution is extended producer responsibility, present from the start: producers, importers and brand owners who introduce plastic packaging into the market bear responsibility for its end-of-life management, working through collection systems, buy-back or deposit arrangements, and registration with the pollution control boards. The Plastic Waste Management Amendment Rules, 2021, notified on 12 August 2021, then did the thing the public knows best: they prohibited the manufacture, import, stocking, distribution, sale and use of identified single use plastic items, chosen for low utility and high littering potential, with effect from 1 July 2022. The identified items include ear buds with plastic sticks, plastic sticks for balloons, plastic flags, candy sticks and ice-cream sticks, polystyrene for decoration, and a range of throwaway articles: plates, cups, glasses, cutlery such as forks, spoons and knives, straws, trays, stirrers, wrapping and packing films around sweet boxes, invitation cards and cigarette packets, and plastic or polyvinyl chloride banners below the prescribed thickness. The same amendment raised the minimum thickness of plastic carry bags, to seventy-five microns from the end of September 2021 and to one hundred and twenty microns from the end of December 2022, on the logic that a thicker bag is worth collecting and recycling. The Guidelines on Extended Producer Responsibility for plastic packaging, notified as the Plastic Waste Management Amendment Rules, 2022 on 16 February 2022, converted the producer obligation into a quantified regime: categories of packaging, targets for recycling and for the use of recycled content, obligations of reuse for rigid packaging, and a market in surplus extended producer responsibility certificates, traded through a centralised online portal maintained by the Central Pollution Control Board, with verification and audit. Extended producer responsibility is the most significant design movement in the whole waste field in a generation, because it shifts a share of the end-of-life cost from the municipality, which never chose the packaging, to the producer, who did.

Did Parliament pass a law banning single use plastic?

No Act of Parliament bans any plastic item. The prohibition on identified single use plastic items was imposed by the Plastic Waste Management Amendment Rules, 2021, made by the Union government under the Environment (Protection) Act, and it took effect from 1 July 2022. The ban is subordinate legislation from beginning to end.

Electronic waste followed the same arc one cycle later. The E-Waste (Management) Rules, 2016, in force from 1 October 2016, built an authorisation-based regime on producers of listed electrical and electronic equipment, with collection targets and extended producer responsibility authorisation from the Central Pollution Control Board. The E-Waste (Management) Rules, 2022, notified on 2 November 2022 and in force from 1 April 2023, replaced them with a registration and certificate regime: manufacturers, producers, refurbishers and recyclers register on the Board’s portal, producers must meet recycling targets that begin at sixty per cent of the quantity of equipment placed on the market in the reference year and rise to eighty per cent, and the targets are discharged by purchasing extended producer responsibility certificates from registered recyclers. The listed equipment grew from twenty-one categories under the 2016 rules to one hundred and six under the 2022 rules.

Construction and demolition waste has its own rulebook, the Construction and Demolition Waste Management Rules, 2016, published on 29 March 2016. They require every generator to segregate construction and demolition waste and deposit it at collection centres or hand it to authorised processing facilities, forbid dumping that obstructs traffic, public space or drains, and cast planning duties on large generators, those producing more than twenty tonnes in a day or three hundred tonnes in a month in a project, who must submit a waste management plan and obtain the local authority’s approval before starting work, segmenting the waste into streams of concrete, soil, steel, wood and plastics, and bricks and mortar. Local authorities must commission processing and recycling facilities and may charge for collection, transport, processing and disposal. Bio-medical waste is governed by the Bio-Medical Waste Management Rules, 2016, which rest on segregation at the point of generation into colour-coded streams, treatment through common bio-medical waste treatment facilities or captive arrangements, authorisation of occupiers and operators by the State boards, and a bar on mixing bio-medical waste with the municipal stream, which is why treated bio-medical waste alone appears inside the solid waste definition in the 2016 Rules. Batteries are governed by the Battery Waste Management Rules, 2022, notified on 24 August 2022, replacing the Batteries (Management and Handling) Rules, 2001: they cover electric vehicle, portable, automotive and industrial batteries, place mandatory extended producer responsibility targets for collection and recycling or refurbishment on producers including importers, and forbid the disposal of waste batteries in landfills. Hazardous and other wastes are governed by the Hazardous and Other Wastes (Management and Transboundary Movement) Rules, 2016, which organise the occupier’s obligations as a hierarchy of prevention, minimisation, reuse, recycling, recovery including co-processing, and safe disposal, under authorisation from the State board, with treatment, storage and disposal facilities as the endpoint; it is into that stream that the domestic hazardous fraction separated under the Solid Waste Management Rules is delivered.

The family resemblance is the analytical point. Every rulebook in the set performs the same three moves: it defines a stream, it allocates duties among generator, producer or occupier, local or facility operator and the boards, and it relies on the parent Act for its offences. The differences are in where the cost is placed. The solid waste rules place the cost on the municipality and, through the user fee, on the resident. The plastic, e-waste and battery rules place a measured share of it on the producer. The hazardous rules place it on the industrial occupier. Reading the family together discloses a legislature-by-delegation feeling its way, stream by stream, towards the question a sanitation and waste statute would have to answer in general terms: who pays for the end of a product’s life, the person who used it, the body that governs the place it was used in, or the enterprise that profited from putting it there.

Extended producer responsibility: the technique that changed the family

Extended producer responsibility deserves a section of its own because it is the one genuinely new legal technique the waste rulebooks have produced, and because its spread from plastic to electronics to batteries shows the rule-making system revising its own theory of where responsibility lies. The principle is easily stated. Where a product’s end of life imposes costs on the public system, the enterprise that placed the product on the market should bear a defined share of those costs, financially or physically, in proportion to what it placed. The principle reverses the default of the municipal model, in which the producer’s interest ended at the sale and the municipality inherited whatever the product became. In the plastic rules the technique began in 2016 as an obligation of effort: producers, importers and brand owners had to work out, with urban local bodies, systems for collecting the plastic waste their products generated, under plans the State boards approved. In the guidelines of 2022 it became an obligation of account: defined categories of plastic packaging, specified recycling targets rising year by year, obligations to use recycled content and to reuse rigid packaging, a centralised online portal administered by the Central Board on which producers, importers, brand owners and plastic waste processors register, and certificates, issued against verified recycling, that can be traded between obligated entities so that a producer short of its target can buy the surplus performance of one that has exceeded it, with environmental compensation for shortfall. In the e-waste rules of 2022 the same architecture appears with recycling targets of sixty per cent rising to eighty per cent of the quantity placed on the market, and in the battery rules with collection and recycling targets across every battery chemistry, coupled with a prohibition on disposal in landfills.

The technique’s legal interest lies in what it does to the enforcement problem. A municipality’s performance is hard to measure and harder to sanction; a producer’s obligation under the certificate system is a number, auditable against portal records, and default is computed rather than proved. The shift moves enforcement from the inspection of conduct to the reconciliation of accounts, and imports into environmental law the instrument family of the market: targets, registries, tradable instruments, compensation for the gap. Its weakness travels with the strength. A certificate system is only as honest as the verification beneath it, and the recycling it certifies is performed substantially by the same informal and small-scale sector the municipal rules struggle to see, reappearing as registered processors whose paperwork the system must trust. The tension between a formal account of recycling and an informal reality of recovery is the frontier on which this technique will either mature or be gamed, and the boards’ annual reporting and the Tribunal’s docket will show which. For the pillar’s argument, the producer responsibility turn is significant for a further reason. It is the system’s own admission, worked out rulebook by rulebook, that the municipal monopoly of responsibility enacted in 2000 was a design error, and that a waste regime functions when the costs of a material are assigned to the actor whose decisions determine the material. That admission, made entirely within delegated legislation, is the most hopeful evidence available that the architecture can learn without waiting for the statute the next sections consider.

The contested kiln: waste to energy and its critics

Within the family of techniques the rules authorise, one has attracted a controversy dense enough to deserve its own account, because it tests the regime’s hierarchy against physics and against neighbourhood politics at once. Waste to energy, the combustion of the combustible fraction for power, or its conversion into refuse derived fuel for cement kilns and power plants, sits in the rules as the destination of last resort before landfill for the dry, high-calorific residue. The Tribunal’s judgment of December 2016 fastened on the condition that makes the technique lawful in spirit: waste must be segregated before it is fed to an energy plant, so that what burns is the fraction that can neither be recycled nor composted, and buffer zones must separate the plant from its neighbours. The condition is not decorative. Indian municipal waste, in the absence of segregation, carries a biodegradable share so high and a moisture content so heavy that its calorific value hovers near the threshold the rules set for the energy route, and a plant fed on mixed waste burns badly, produces emissions its neighbours can smell and measure, and leaves a larger residue of ash and unburnt matter than its design promised.

The case for the energy route, made by its project developers and by land-starved city governments, is arithmetic of a different kind. A metropolitan city that has exhausted its landfill geography, whose dumps have grown into hills and whose search for a fresh site has failed against neighbourhood resistance for a decade, faces a daily tonnage that must go somewhere on the day it arises. Composting absorbs the wet fraction, recycling the recoverable dry fraction, but a residual combustible stream remains whose volume only combustion reduces decisively, and a waste to energy plant converts that stream into electricity and a fraction of its weight in ash, on a footprint far smaller than a landfill of equivalent capacity. The power ministry’s duties in the rules, tariff determination and compulsory purchase of the power by distribution companies, together with the renewable energy ministry’s subsidies, exist precisely to make that arithmetic bankable, because waste to energy power is expensive power and no distribution company would buy it voluntarily at the tariff the plant requires.

The case against, made most persistently by the Centre for Science and Environment in its assessments of the sector and by the residents’ associations that live beside the plants, is that the technique is being asked to solve the wrong problem in the Indian setting. A plant is a hungry asset: financed on a contracted tonnage, it needs the waste to keep coming, which inverts the regime’s hierarchy by giving the city a commercial reason to keep generating a combustible stream rather than shrinking it through segregation and recovery. Its emissions discipline depends on flue gas treatment operated to standard every day, supervised by boards whose inspection capacity is thin. And its economics, the critics argue, conceal a transfer: the tipping fee the municipality pays per tonne, plus the power subsidy, plus the land at nominal value, amount to a public subvention of a technology whose alternatives, decentralised composting and material recovery, employ more people per tonne and fail more gracefully when they fail. The residents beside the older plants add the evidence of their senses, the odour, the ash, the truck traffic, and their litigation has repeatedly reached the Tribunal, which has generally allowed plants to operate under tightened conditions rather than close them, while insisting on the segregation and buffer conditions of the judgment. The honest summary is that waste to energy is a lawful and sometimes necessary instrument for the residual stream of a large city, being sold in some projects as a solution for the whole stream of any city, and that the rules, read with the Tribunal’s conditions, support the first proposition and not the second. The distinction matters to every reader who meets a plant proposal in a municipal council agenda, because the legal question is never whether a city may burn waste. It is whether what the city proposes to burn is the fraction the law reserves for burning.

The other half of sanitation: sewage, septage and sludge

The title of this article promises urban sanitation, and an honest treatment must record that solid waste, its subject so far, is only the dry half of it. The wet half, the sewage from water closets and drains, the septage pumped from septic tanks, the faecal sludge of a city most of whose buildings are not connected to a sewer network at all, is governed by a different and even more fragmented arrangement, and the fragmentation is itself evidence for the article’s thesis. No statute governs urban liquid waste as a municipal service either. Sewage treatment plants operate under consent from the State pollution control boards under the Water (Prevention and Control of Pollution) Act, 1974, discharging to standards the boards prescribe and enforce as industrial-style consents, although the discharger is a municipality and the effluent is a city’s. The underground sewerage network, where it exists, is a municipal function under the State Acts, financed substantially by mission money: the Atal Mission for Rejuvenation and Urban Transformation and, for cities below one lakh population, the Used Water Management component added in the second phase of the Swachh Bharat Mission, Urban, which funds sewage and septage infrastructure in the towns the sewerage programmes had not reached. Faecal sludge and septage management, the discipline of emptying, transporting, treating and safely disposing of the contents of septic tanks and pits, rests at the national level on a policy, the National Policy on Faecal Sludge and Septage Management issued by the urban development ministry in 2017, which is guidance to States and cities and creates no enforceable duties at all, supplemented in many States by State-level faecal sludge regulations and by municipal bye-laws of uneven reach.

The worker’s position binds the two halves together. The septic tank and the sewer are where sanitation work kills, and the legal instruments that address that danger sit outside the waste rulebooks entirely: the prohibition statute of 2013, which forbids hazardous manual cleaning and is examined at headline level in the next section, and the general criminal and compensation law that is invoked after a death. A legal map of urban sanitation drawn only from the solid waste rules would miss the fact that the deadliest task in the sector is governed by a social justice statute, funded by no mission component of comparable weight, and monitored by no tribunal docket of comparable intensity. The dry half of sanitation has a rulebook, a mission, annual reporting and a compensation jurisprudence. The wet half has consents, policies and schemes. If the argument of this article is that the form of the instrument decides the quality of the accountability, the comparison between the two halves is its strongest exhibit, because the half with the fuller legal apparatus is also the half whose failures are measured, reported and priced, while the half governed by policy alone produces failures that surface mainly as funerals.

The people who handle the waste

No account of this body of law is honest if it treats waste as a flow of material only. It is also a flow of labour, performed by municipal sanitation workers, by contract workers engaged through the agencies to whom municipalities outsource collection, and by the informal workforce of waste pickers and itinerant buyers who recover recyclables from doorsteps, bins, streets, material recovery facilities and dumpsites. The 2016 Rules acknowledge that workforce with unusual care for an environmental instrument. Waste pickers are defined in the rules, as persons informally engaged in the collection and recovery of reusable and recyclable waste for sale to recyclers, directly or through intermediaries, to earn their livelihood. The State policy that each State must prepare is directed to acknowledge the primary role played by the informal sector in reducing waste and to give broad guidelines for its integration. The State urban development secretary must start a scheme for the registration of waste pickers and waste dealers. The State Level Advisory Body that reviews implementation includes a representative of a non-governmental organisation or civil society body working for waste pickers and the informal recycling sector. At the municipal end, Rule 15 requires the system of recognition, the self help groups, the identity cards, the access to material recovery facilities and the training, and Rule 11’s companion duties at State level and Rule 15’s protective equipment clause reach the workers’ bodies as well as their status.

The honest record, as the brief for this article insists, is that this recognition has been implemented unevenly. Where a city has organised its waste pickers into cooperatives or self help groups with identity cards, door to door routes and access to dry waste collection centres, integration is a fact and incomes have a floor. Where recognition remains a paragraph in a State policy, the waste picker continues to work the dumpsite and the street bin without status, and the arrival of a private concessionaire with an exclusive collection contract can extinguish the informal worker’s access to the same material the rules say she must be integrated to collect. The people performing the most hazardous parts of this work, the manual handling of mixed waste, the sorting of streams that contain needles, broken glass and sanitary waste, the cleaning of drains and sewers, stand largely outside the employment statutes: no appointment, no provident fund discipline, no compensation regime designed for them, their protection assembled from the protective equipment clause of an environmental rulebook, the general law and the specific prohibition statute considered next.

That statute is the Prohibition of Employment as Manual Scavengers and their Rehabilitation Act, 2013, Parliament’s enactment forbidding the manual cleaning of sewers, septic tanks and insanitary latrines and providing for the rehabilitation of persons identified as manual scavengers, treated at headline level here because the series account of the manual scavenging Act of 2013 owns its provisions. Its place in this article is structural. The sanitation cluster in social justice law and the sanitation rules in environmental law govern the same human activity from opposite ends: the 2013 Act addresses the worker and the indignity and danger of the work, the 2016 Rules address the material and the systems that should make the dangerous forms of the work unnecessary, since a city with segregated collection, mechanical handling and lawful processing has less need for a worker inside a drain than a city without them. The two instruments meet in the person of the sanitation worker, and the distance between their promises and the record of deaths in sewers and septic tanks is the sharpest single measure of how far the formal law of sanitation runs ahead of its administration.

The document trail: where the system’s record actually lives

For the researcher, the archivist and the practitioner, a pillar treatment should end its description of the machinery by marking where its records are, since in this field the operative truth is distributed across a chain of publications rather than concentrated in the rulebook. The first layer is the rulebooks themselves, read in their amended form: the Solid Waste Management Rules, 2016 with their two Schedules, and the parallel plastic, e-waste, construction and demolition, bio-medical, battery and hazardous rulebooks, each carrying its own duties for the streams it owns. The second layer is the State’s: the State policy and strategy prepared under Rule 11, the State annual reports that the pollution control boards consolidate from local returns, and the Central Board’s annual consolidated report on implementation, which gathers the State reports into the national implementation picture of generation, collection, treatment and disposal and of the authorisations granted and refused. The third layer is the adjudicatory record: the Almitra Patel proceedings and their transfer order, the principal judgment of December 2016 in Original Application No. 199 of 2014, and the execution proceedings in Original Application No. 606 of 2018 with the State-wise compensation orders of 2022, which together constitute the fullest judicial account of the system’s condition that exists. The fourth layer is the mission’s: the Swachh Bharat Mission guidelines and their second-phase successor, the annual Swachh Survekshan rankings, and the mission’s reporting on legacy dumpsite remediation, which supply the funding and performance figures against which the legal duties must be read. The fifth layer is the city’s own paper: the bye-laws that alone bind the resident, the authorisation of the local facility with its conditions, and the local body’s annual report, which Rule 15 requires to be prepared by the thirtieth of April and forwarded upward through the district and board chain. A question about waste law in India is almost never answerable from one layer, and the professional skill this article most hopes to transmit is the habit of asking, for any proposition about the system, which layer would show it, and going there.

Enforcement: boards, penalties and the Tribunal

The enforcement design of the rules is a reporting pyramid topped by two coercive instruments, a penalty and a tribunal. Begin with the pyramid. The operator of a facility reports annually to the local body. The local body reports annually to the State pollution control board and to the State urban development department. Each State board prepares a consolidated annual report for the Central Pollution Control Board, which prepares a consolidated annual review of implementation across the country and forwards it, with recommendations, to the urban affairs and environment ministries, and the whole is reviewed in the central monitoring committee. The State Level Advisory Body in each State reviews implementation every six months. On paper, therefore, the state of every city’s waste is supposed to ascend, once a year, from the facility gate to the Union ministry. In practice the Central Board’s annual reports have recorded, year after year, the pattern the Tribunal later priced: generation rising, collection high on paper, processing lagging collection by a wide margin, and legacy waste accumulating in dumpsites that the rules required to be bio-mined or capped. The pyramid transmits information faithfully. What it cannot transmit is capacity, and information about a failure, however regular, is not a remedy for it.

The first coercive instrument is the authorisation. Waste facilities, and local bodies handling more than five tonnes a day, operate under authorisation from the State pollution control board, which may suspend or cancel the authorisation of a defaulting operator after notice, and which is charged with enforcing the rules through the local bodies and reviewing implementation at least twice a year. The second is the penalty of the parent Act. A contravention of the Environment (Protection) Act or of rules made under it was, in the Act as enacted, punishable under Section 15 with imprisonment for a term extending to five years, or fine extending to one lakh rupees, or both, with an additional fine for every day of continuing failure and a longer term, extending to seven years, where the failure continued beyond a year after conviction. Prosecutions of municipalities under that clause were always a theoretical rather than a practical instrument, since the criminal process against an elected local government for a service failure is a remedy no prosecutor reaches for, and the Jan Vishwas (Amendment of Provisions) Act, 2023 has since recast the parent Act’s penal scheme in monetary form: from 1 April 2024 the substituted scheme works through penalties running from ten thousand rupees to fifteen lakh rupees, imposed by adjudicating officers with an appeal to the National Green Tribunal and the proceeds credited to an Environmental Protection Fund. The Supreme Court, in the M. C. Mehta proceedings in October 2024, observed that the substituted Section 15 had been rendered toothless because the adjudicating machinery to work it had not been put in place, and recorded the assurance of the Additional Solicitor General that the machinery would be in existence within weeks. The episode is a small parable of the whole field: the sanction exists, the machinery to move it lags, and in the interval the duty floats free of its consequence.

The instrument that has actually moved is the third one, the Tribunal. The supervision of municipal waste passed to the National Green Tribunal when the Supreme Court transferred the Almitra Patel proceedings to it in September 2014, and the Tribunal, whose constituting statute is treated in the account of the National Green Tribunal Act 2010, delivered its principal judgment in Original Application No. 199 of 2014 on 22 December 2016. The judgment directed all States and local authorities to comply with the Solid Waste Management Rules, 2016 without delay, imposed a complete ban on the open burning of waste, required segregation before waste is fed to waste to energy plants, directed that landfills receive only inert and residual waste, called for buffer zones around plants and landfill sites, required action plans from the States, and warned that inaction would invite prosecution of the responsible authorities and environmental compensation. Execution proceedings followed, in the matter carried under the title Compliance of Municipal Solid Waste Management Rules, 2016, in which the Tribunal reviewed State after State against the Central Board’s annual reporting. In 2022 the Tribunal converted supervision into price. Acting under Section 15 of the National Green Tribunal Act and computing compensation on the polluter pays principle at two crore rupees for every million litres a day of untreated sewage and three hundred rupees for every tonne of unprocessed legacy waste, it levied environmental compensation on State after State: Rs 12,000 crore on Maharashtra, of which about Rs 10,840 crore answered the sewage treatment gap and about Rs 1,200 crore the un-remediated legacy waste, Rs 3,800 crore on Telangana, Rs 3,500 crore on West Bengal, which deposited the amount in the ring-fenced account the Tribunal directed, Rs 3,000 crore on Rajasthan and Rs 2,900 crore on Karnataka, with smaller levies elsewhere, the year’s levies exceeding Rs 28,000 crore in aggregate. The Supreme Court later stayed the Maharashtra levy, as it did the Rajasthan one, with proceedings continuing. The compensation is not a fine paid away; the Tribunal directed deposit in separate ring-fenced accounts to be operated under the Chief Secretary’s directions and spent on restoration measures, sewage treatment, processing plants and the remediation of dumpsites. The municipality’s accountability for waste thus runs, in the operative sense, to a tribunal that prices its failure and sequesters the price for the works the failure omitted.

The whole structure can be held in one view in the artifact below, which sets out, for each actor in the system, the duty owed, the instrument that imposes it, the authority that enforces it and the sanction that backs it. Read down the enforcement column and the article’s argument makes itself: the household’s duty is enforced by a bye-law fine almost never levied, the producer’s by a registration and certificate regime with a market in it, and the local authority’s, the heaviest duty of all, by a tribunal.

Actor	Duty	Instrument imposing it	Enforced by	Sanction
Household and waste generator	Segregate waste into biodegradable, non-biodegradable and domestic hazardous streams; hand over to authorised collectors; pay the user fee; not throw, burn or bury waste in streets, drains or water bodies	Rule 4 of the Solid Waste Management Rules, 2016; municipal bye-laws	Local body officers authorised under the bye-laws	Spot fine for littering and non-segregation fixed in the bye-laws; in practice levied rarely
Bulk generator	Segregate at institutional scale; process biodegradable waste within the premises as far as possible, in partnership with the local body	Rule 4 of the Solid Waste Management Rules, 2016	Local body; State pollution control board through facility authorisation	Bye-law fine; penalty under the Environment (Protection) Act
Waste picker	None cast as a duty; the rules confer recognition, identity cards, training and access to material recovery facilities	Rules 11 and 15 of the Solid Waste Management Rules, 2016	Local body and State urban development department, as duty-bearers towards the worker	None against the worker; the enforceable duties run the other way, and their breach is a service failure
Local authority	Prepare the waste plan; collect door to door; set up material recovery and processing facilities; landfill residual waste only; bio-mine or cap old dumps; frame bye-laws and spot fine criteria	Rule 15 and Rule 22 of the Solid Waste Management Rules, 2016; State municipal Act	State pollution control board; National Green Tribunal	Suspension or cancellation of facility authorisation; environmental compensation levied on the State and authority
State pollution control board	Enforce the rules through local bodies; grant, renew, suspend facility authorisations; monitor standards in Schedules I and II; consolidate annual reports	Rule 16 and Rule 24 of the Solid Waste Management Rules, 2016	Central Pollution Control Board; National Green Tribunal	Tribunal directions in the compliance proceedings; no direct penalty on the board
State government	Prepare the State policy and strategy within one year; allocate land for facilities; constitute the State Level Advisory Body; start registration of waste pickers	Rules 11 and 23 of the Solid Waste Management Rules, 2016	Central monitoring committee; National Green Tribunal	Environmental compensation levied on the State, as in the levies of 2022, payable into a ring-fenced restoration account

A resident who has absorbed the table knows where a complaint goes, and the general position can be stated plainly. The complaint about uncollected waste lies first to the local body, which owes the collection duty and runs the grievance machinery of the mission; it lies next to the State pollution control board, which enforces the rules through the local body; and it lies, at the end of the chain, to the National Green Tribunal, which has entertained the subject at the scale of whole States. The account in this article is a general description of that architecture; the position in any individual dispute, about a fee, a fine or a facility, turns on the bye-laws and records of the local body concerned and on the authorisations in force for it, which are matters for advice on those documents.

The resident in court: neighbourhood litigation and the facility next door

A complete account must also place the resident in the courtroom, because residents appear in this field in two opposite postures and the case law holds both. In the first posture the resident is the prosecutor of the system: the Ratlam complainants whose persistence produced the foundational doctrine, the petitioners of the Almitra Patel litigation, and the applicants in the Tribunal proceedings who compel a defaulting municipality to collect, transport and stop the burning. In this posture the citizen’s right to a clean environment, read into Article 21 by four decades of constitutional jurisprudence, is the lever, and the courts have consistently received it, treating the statutory duty of the local body as the correlate of the citizen’s right and refusing to let impecuniosity answer either. In the second posture the resident is the defendant of his own street: the neighbourhood that opposes the siting of the transfer station, the processing plant or the landfill at its edge, organising through the residents’ welfare association, litigating the authorisation, the buffer zone, the distance from the habitation and the environmental clearance. Here the courts and the Tribunal have been equally consistent in the other direction. A facility that the rules authorise, sited on land the State has allotted, at the distances the Schedules prescribe, and operated within its standards, will not be wished away because its neighbours dislike it; the Tribunal’s pattern has been to test the facility against the rulebook, order the defects corrected, impose the buffer and monitoring conditions, and decline the closure the neighbourhood seeks. Waste must go somewhere is not a legal proposition, but it is the factual premise every siting judgment quietly adopts, and the alternative to a lawful facility is rarely the absence of waste. It is the unlawful dump, which arrives without authorisation, buffer or monitoring in the same or a poorer neighbourhood.

The two postures together explain the politics that the municipal case in the next section describes. A city administration that enforces segregation against its residents, charges them the fee, fines the thrower and sites the facility, accumulates opposition from every direction at once, while an administration that under-provides the service faces only the diffuse risk of a tribunal proceeding in which the penalty is paid from public funds. The legal architecture, in other words, prices political courage higher than political neglect, and any reform that ignores that pricing will be defeated by it. The resident reader should take from this section the location of their own leverage. It lies in the documents: the authorisation and its conditions, the annual report the local body must file, the bye-laws whose fees and fines are public law, and the board’s monitoring record, all of which are obtainable and quotable, and which convert a grievance about smell and smoke into a case about specified duties. The Tribunal’s waste docket was built by applicants who learned to plead the rulebook rather than the nuisance, and the rulebook rewards being read.

The two cases, stated at full strength

The municipal case deserves to be put as its strongest advocates put it, because it is substantially an argument about arithmetic. Segregated collection requires a fleet, and a fleet of compartmentalised vehicles costs capital and then costs again in fuel, crews and maintenance every day it runs. Processing requires land, which in a dense city is the scarcest input of all, and plants, whose capital cost per tonne of capacity dwarfs the annual sanitation budget of a small municipality. A sanitary landfill built to Schedule I, with liners, leachate management, buffer zones and a closure plan for a working life of twenty to twenty-five years, is an engineering project of a scale most local bodies have never executed. Against these requirements, municipal own revenue is thin: the property tax, the mainstay, is levied on outdated assessments and collected partially, user charges for waste are nominal where they exist, and the State transfers and mission grants that fill the gap arrive tied to programme designs and timelines the local body does not control. The rules were framed without a corresponding funding mechanism, and the States said so, in substance, in the Tribunal proceedings, where government after government pointed to cluster arrangements, plants under construction and proposals in process as evidence that the constraint was capacity and sequence rather than will. When environmental compensation is then levied for the shortfall, the municipal argument completes itself: the compensation is drawn from the same public funds that finance the service, so the penalty consumes the means of its own cure, and a State ordered to deposit thousands of crores in a restoration account is a State whose general revenues, from which municipal support also comes, are reduced by that amount. On this view the regime mistakes a finance and capacity failure for a compliance failure, and punishes the second because it cannot repair the first.

The environmental case is equally strong, and it begins from the body rather than the budget. Unmanaged waste is not an aesthetic deficit. It is leachate in the ground water, methane and smoke from burning dumps, drains blocked against the monsoon, vectors breeding at the collection point that was never built, and a daily occupational exposure borne by the workers and the neighbourhoods, usually the poorest in the city, that live beside the dumpsite. The harm is immediate, it is unequally distributed, and it compounds: every year of unprocessed accumulation enlarges the legacy mountain that a later administration must bio-mine at multiples of the cost of processing the waste when it arose. Against the plea of incapacity, the environmental side answers from the record. The rules in their modern form date from 2016, and their predecessor from 2000; the timelines were set by the rulebook itself and extended by the Tribunal’s patience across years of execution proceedings. A local body which has not framed its bye-laws, has not prescribed or collected the user fee its own rules empower, has not used the mission money on offer, and has not enforced segregation against its bulk generators has not exhausted its remedies, and its plea of poverty is the plea Ratlam rejected in 1980, that a statutory duty dissolves in the face of an unwilling budget. The pollution control boards’ annual reporting shows cities of comparable means performing markedly differently, which is evidence that administration, and not only money, is a variable in the outcome. On this view, compensation is not a punishment but the polluter pays principle applied to the largest polluter in the field, which is the State that under-provides the service, and the ring-fencing of the amount for restoration prevents the levy from being absorbed as a general fiscal event.

Both cases are substantially correct, and the article’s verdict has to hold them together rather than choose between them. The municipal case is right about the instrument: a rulebook without a funding mechanism, enforced by compensation drawn from the service’s own fiscal base, will reproduce the failure it prices. The environmental case is right about the duty: the harm is real, the timelines were generous, and the plea of incapacity has been available for so long that it has become part of the machinery of postponement. What the two cases share, and what neither side’s advocacy reaches, is the design defect underneath both. The duty, the money and the sanction belong to three different instruments and three different authorities, so no single institution owns the outcome. The urban affairs ministry owns the money programme but not the rules. The environment ministry owns the rules but not the money or the municipalities. The State owns the municipalities but did not write the duties. The Tribunal owns the sanction but neither budgets nor administers. A system so arranged can generate directions, reports and levies indefinitely without generating the service, because each participant can truthfully say that the missing element is another participant’s.

The demand for a sanitation statute

It is against that diagnosis that the recurring demand for a national sanitation statute has to be assessed. Such a statute is periodically proposed, in committee reports, in professional commentary and in the manifestos of municipal reform, and its advocates argue from the gap this article has described: waste and sanitation are governed by delegated legislation under an Act about something else, and a subject that touches public health in every street deserves primary legislation. The demand is coherent, but a statute is not a spell. Setting out what an Indian sanitation Act would actually have to resolve is the honest way to test it.

It would have to settle the constitutional question first. Sanitation and local government are State subjects, so a Union statute would need either the consent route of Article 252, with States adopting it, or the treaty-implementation route of Article 253 that carries the Environment (Protection) Act, or a constitutional amendment moving or sharing the subject; each route writes a different federal bargain into the law, and the choice among them is a political decision no drafting can evade. It would have to assign the money: a sanitation statute that did not earmark a revenue source, a share of a tax, a formula of transfers or a power and duty to levy user charges with floors and indexation would reproduce, in grander form, the central defect of the rules. It would have to decide who regulates the municipality as a service provider: whether the pollution control boards continue to supervise a public service as though it were an emission source, or whether a service regulator, with jurisdiction over standards, tariffs and performance and with the municipality as a regulated utility, is the better instrument. It would have to give the household’s duties a statutory form with proportionate, collectable sanctions and the procedural protections that attach to penalties, replacing the patchwork of dormant bye-law fines. And it would have to settle the status of the sanitation workforce, bringing contract and informal workers within an employment and safety framework rather than leaving their protection to clauses in an environmental rulebook and a prohibition statute. A bill that resolved those five questions would be a major work of legislation. A bill that merely re-enacted the duties of the 2016 Rules in statutory form would change nothing except the citation, and readers who meet the demand for a statute in public debate are equipped, after this article, to ask which of the two is being proposed.

Verdict

The verdict of this pillar is the proposition stated at its opening, tested against the rulebook’s text, the funding record and the enforcement history. India regulates municipal waste through rules made under an environmental Act, and those rules impose obligations on municipalities that municipal law does not fund and on households that municipal bye-laws barely enforce, so the instrument that creates the duty, the instrument that provides the money and the instrument that enforces the sanction are three different things answering to three different authorities. The rules themselves, read closely, are better than their reputation: the segregation duty is well aimed, the landfill’s demotion to a destination for residues is sound policy honestly drafted, the recognition of waste pickers is a genuine first in national law, and the parallel rulebooks’ turn to extended producer responsibility shows the system learning to place costs on the actor who creates them. What fails is not the drafting but the architecture, and architecture is the one thing delegated legislation cannot rebuild. The reader who needs the law in action should therefore hold three documents together: the Solid Waste Management Rules, 2016 for the duties, the bye-laws of the city in question for the fees and fines that actually bind the resident, and the mission and tribunal record for the money and the pressure. No one of the three is the law of sanitation alone. Together, they are all of it that there is.

Frequently Asked Questions

Q: Which law governs solid waste management in India?

No single statute governs it. The field is regulated by the Solid Waste Management Rules, 2016, made by the Union government under Sections 3, 6 and 25 of the Environment (Protection) Act, 1986, which superseded the Municipal Solid Wastes (Management and Handling) Rules, 2000. Around that rulebook stand the State municipal Acts, which assign sanitation to municipalities as an obligatory function, the municipal bye-laws framed under them, which set the user fees and fines that bind residents, and the parallel rulebooks for plastic, electronic, bio-medical, construction and demolition, battery and hazardous waste. The constitutional setting is supplied by the Seventy-fourth Amendment and the Twelfth Schedule, which list public health, sanitation conservancy and solid waste management among the functions that may be devolved to municipalities.

Q: What duties does a waste generator have?

Rule 4 of the Solid Waste Management Rules, 2016 casts them. Every generator must segregate waste at source into three streams, biodegradable waste, non-biodegradable waste and domestic hazardous waste, store them in separate bins and hand them over to the authorised collectors engaged by the local body; wrap sanitary waste securely before placing it in the dry bin; store construction and horticulture waste separately within the premises and dispose of it by the local body’s directions; and refrain from throwing, burning or burying waste on streets, open public spaces, drains and water bodies. The generator pays the user fee the bye-laws prescribe, carries reusable bags to displace plastic carry bags, and, for gatherings above one hundred persons, intimates the local body and arranges segregation and handover at the venue.

Q: What must a municipality do about waste?

Rule 15 of the 2016 Rules sets the chain. The local authority must prepare a solid waste management plan, frame bye-laws prescribing user fees and spot fines, collect segregated waste door to door including from slums and informal settlements, run public awareness programmes, facilitate material recovery facilities, arrange transport in covered and compartmentalised vehicles, build processing facilities with preference for decentralised and biological methods, send only residual and inert waste to sanitary landfills, provide deposition centres for domestic hazardous waste, integrate authorised waste pickers and self help groups with identity cards, remediate or cap old dumps, obtain the State board’s authorisation where its waste exceeds five tonnes a day, and file its annual report by 30 April. Rule 22 sets the timeframes for each element.

Q: Which separate rules cover plastic and electronic waste?

Plastic waste is governed by the Plastic Waste Management Rules, 2016, as amended. The 2021 amendments prohibited identified single use plastic items from 1 July 2022 and raised carry bag thickness in stages to 120 microns, and the 2022 guidelines built an extended producer responsibility regime for plastic packaging, with categories, recycling targets and tradable certificates administered through a centralised portal. Electronic waste is governed by the E-Waste (Management) Rules, 2022, in force from 1 April 2023, which replaced the 2016 rules, extended coverage to 106 categories of electrical and electronic equipment, and require producers to meet recycling targets rising from sixty to eighty per cent through registered recyclers and certificates. Both rulebooks are made under the Environment (Protection) Act, 1986.

Q: Can a resident be fined for not segregating waste?

Yes, but the fine reaches the resident through the municipality’s bye-laws rather than directly under the 2016 Rules. Rule 15 requires every local authority to frame bye-laws prescribing user fees for waste services and criteria for levying spot fines for littering, and the State municipal Acts supply the penalty machinery for breach of bye-laws. Where a city has framed and notified its bye-laws under the 2016 framework, its sanitation staff may fine a resident who refuses to segregate, throws waste in a public place, or fails to hand over waste in the prescribed streams, and repeat defaults can be prosecuted under the municipal Act. The practical position varies sharply by city, since many municipalities enforce the fee and fine schedules weakly or not at all, but the legal power exists wherever the bye-law has been made.

Q: Who enforces the waste rules and how?

The State pollution control boards enforce the rules through the local bodies under Rule 16, granting and renewing authorisations for facilities, monitoring the standards in the Schedules and reporting upward; the Central Pollution Control Board coordinates the State boards, frames standards and consolidates the annual implementation picture under Rule 14. The District Magistrate reviews the local bodies’ performance quarterly under Rule 12. Behind the boards stand the coercive instruments of the Environment (Protection) Act: directions under Section 5, enforceable by closure and stoppage of utilities through the rules made for that purpose, and monetary penalties under the substituted Section 15, imposed by adjudicating officers with an appeal to the National Green Tribunal. The Tribunal itself supervises compliance in its execution proceedings and has levied environmental compensation on defaulting States, and the constitutional courts retain their Article 21 jurisdiction.

Q: Why is sanitation regulated through environmental rules?

Because the constitutional allocation made it the available route. Public health and sanitation, and local government, are State subjects under Entries 6 and 5 of List II, so Parliament had no direct power to enact a municipal sanitation code for the States. What the Union possessed was the Environment (Protection) Act, 1986, enacted under Article 253 to implement international environmental commitments, whose rule-making power reaches any environmental matter including the handling of waste. When the Supreme Court’s waste litigation of the 1990s demanded national standards, the executive answered with rules under that Act, first in 2000 and again in 2016, treating municipal waste as an environmental pollutant to be handled rather than as a municipal service to be organised. The Twelfth Schedule’s listing of sanitation among municipal functions is permissive, depending on State legislation for its force, so the environmental route remained the only uniform national instrument.

Q: What have the courts directed on waste management?

The Supreme Court held in Municipal Council, Ratlam v. Vardhichand (1980) that a municipality’s financial inability is no defence to its statutory duty to provide sanitation. In the Almitra H. Patel proceedings from 1996, the Court monitored municipal waste nationally, received the Burman Committee’s report, and saw the first national rules follow in 2000, before transferring supervision to the National Green Tribunal on 2 September 2014. The Tribunal’s judgment of 22 December 2016 in Original Application No. 199 of 2014 directed implementation of the 2016 Rules, banned open burning, required segregation before waste to energy plants, confined landfills to inert and residual waste and ordered action plans, with prosecution and compensation for inaction. In the execution proceedings that followed, the Tribunal levied environmental compensation on defaulting States computed by untreated sewage gap and unprocessed legacy waste, directing the amounts into ring-fenced restoration accounts.

Q: What changed between the Municipal Solid Waste Rules of 2000 and the Solid Waste Management Rules of 2016?

Almost every load-bearing element. The 2000 Rules bound municipal authorities alone and stopped at the municipal boundary; the 2016 Rules extend to outgrowths, census towns, notified areas, industrial townships, railways, airports, ports, defence establishments, special economic zones and notified pilgrimage places. The 2000 Rules placed nearly every duty on the municipality; the 2016 Rules cast detailed duties on waste generators, bulk generators, State governments, district administrations and manufacturers. Source segregation into three streams became the generator’s legal duty. Processing and recovery moved to the centre, with the sanitary landfill demoted to a destination for residual and inert waste alone. Waste pickers entered national law for the first time, with recognition, identity cards and integration into collection. And the compliance calendar of staged deadlines was replaced by the timeframes of Rule 22, running from six months to five years by subject.

Q: What is a bulk waste generator under the 2016 Rules?

Rule 3 defines the term by a list of institutional occupants: offices of the Union and State governments and their undertakings and public sector bodies, local bodies themselves, commercial establishments including malls, airports, railway and bus stations, ports, educational and religious institutions, and premises of companies and societies, in each case where the average waste generated exceeds one hundred kilograms per day. The definition matters because the heavier duties attach to it. A bulk generator must segregate in the three streams and ensure its waste is collected, transported and disposed of in partnership with the local authority, and the large institutional campuses that the generator chapter addresses, residents’ welfare associations and gated communities above five thousand square metres, hotels and restaurants, must process their biodegradable fraction within their premises as far as possible.

Q: What is a material recovery facility and who must set one up?

A material recovery facility is defined in Rule 3 as a facility where non-compostable solid waste can be stored and segregated by authorised informal and formal recyclers for onward use, recycling or recovery. Rule 15 makes the local authority responsible for facilitating the construction, operation and maintenance of such facilities, directly or through agencies, so that the dry stream collected door to door has a lawful sorting destination. The facility is where the rules’ recognition of the informal sector becomes operational: authorised waste pickers and informal waste collectors must be given access to sort the material, and the facility may be franchised to a self help group, a company or an entrepreneur, who may charge user fees with the local body’s approval for upkeep, while paying prescribed wages and observing the industrial safety measures the rules require of every facility operator.

Q: What waste is allowed to go into a sanitary landfill?

Only the fraction that nothing else can use. The rules define residual solid waste as the waste and rejects from processing facilities that is not suitable for recycling or further processing, and Rule 15 directs that facilities be set up so that only residual and inert waste reaches the landfill, with the landfill developed for that diet under the specifications of Schedule I. In practice the lawful contents are processing rejects, inert material such as street sweepings and silt after dust removal, and stabilised residues. Two streams are excluded by rule in terms: recyclable material, which belongs in recovery, and non-recyclable waste with a calorific value of fifteen hundred kilocalories per kilogram or more, which must go to energy generation, refuse derived fuel or co-processing and shall not be landfilled. Mixed unsegregated waste has no lawful place there at all.

Q: What is extended producer responsibility for plastic packaging?

It is the obligation the plastic rules place on the enterprises that place plastic packaging on the market to answer for its end of life. The Extended Producer Responsibility Guidelines, notified as the Plastic Waste Management (Amendment) Rules, 2022 on 16 February 2022, divide plastic packaging into categories, rigid, flexible, multi-layered and compostable among them, and set the obligated producers, importers and brand owners targets for recycling, for the use of recycled content and for the reuse of rigid packaging, rising year by year. Performance is evidenced by certificates issued by registered plastic waste processors and traded between obligated entities through the centralised online portal administered by the Central Pollution Control Board, which also registers every obligated entity and processor, and shortfalls attract environmental compensation. The technique converts a collection problem into an auditable account measured against what each enterprise sold.

Q: Which single use plastic items are banned in India?

The Plastic Waste Management (Amendment) Rules, 2021, notified on 12 August 2021, prohibited the manufacture, import, stocking, distribution, sale and use of identified single use plastic items from 1 July 2022, on the ground of their low utility and high littering potential. The list runs to ear buds with plastic sticks, plastic sticks for balloons, plastic flags, candy sticks, ice-cream sticks, polystyrene for decoration, plates, cups, glasses, cutlery such as forks, spoons and knives, straws, trays, stirrers, wrapping and packing films around sweet boxes, invitation cards and cigarette packets, and plastic or polyvinyl chloride banners below the prescribed thickness. Separately, the minimum thickness of plastic carry bags was raised to seventy-five microns from the end of September 2021 and to one hundred and twenty microns from the end of December 2022, and enforcement rests with the State boards and local authorities.

Q: What does the Swachh Bharat Mission have to do with waste law?

The Mission is the money beside the rules. The Solid Waste Management Rules create the duties; the Swachh Bharat Mission, Urban, launched on 2 October 2014 as a programme rather than a statute, financed the infrastructure the duties require, and its second phase from 2021 to 2026, with a total outlay of Rs 1,41,600 crore including committed central assistance of Rs 36,465 crore, set the vision of garbage free cities and undertook the remediation of all legacy dumpsites. The Mission’s annual city ranking, the Swachh Survekshan, supplies the comparative performance pressure that operates alongside legal enforcement. The relationship explains a recurring feature of the field: a city may be in breach of the rules and in receipt of mission funds at the same time, because the two instruments answer to different ministries and measure different things, one the duty and the other the progress.

Q: What is legacy waste and why must it be bio-mined or capped?

Legacy waste is the accumulated municipal waste of past years lying in dumpsites across the country, mixed, partially decomposed and intermixed with soil and inert material, deposited over decades during which dumping rather than processing was the practice. Rule 22 required the remediation of old and abandoned sites to be completed within five years, and Rule 15 prescribes the two lawful routes: bio-mining or bio-remediation, in which the heap is excavated, screened and separated into soil-like material, recyclables, combustibles for refuse derived fuel and inerts, recovering the land beneath; or, where investigation establishes that bio-mining is not feasible, scientific capping of the site in accordance with the landfill closure specifications. The National Green Tribunal priced unprocessed legacy waste at Rs 300 per tonne in its compensation orders against defaulting States, and the second phase of the Swachh Bharat Mission made the remediation of all legacy dumpsites a national undertaking.

Q: How can a resident complain about uncollected garbage?

The first channel is the municipality itself. Every local body maintains a grievance system for its obligatory functions, through the ward office, a helpline or the municipal corporation’s complaint portal, and uncollected waste, a missed collection round or a neighbourhood dump are complaints the local authority is under a duty to answer, since collection is its Rule 15 obligation. The Swachh Bharat Mission operates a dedicated grievance application, the Swachhata application, through which a resident may lodge a photographed complaint that is routed to the responsible municipal officer with an escalation trail. Beyond the city, a complaint about systemic failure, an unauthorised dump, a burning site or a facility breaching its standards, may be made to the State pollution control board, which holds the monitoring and authorisation powers, and a resident or a residents’ association may carry a substantial environmental default to the National Green Tribunal, whose waste docket was built by such applicants.

Q: What penalty applies for breaking the waste rules made under the Environment (Protection) Act?

The answer changed on 1 April 2024. As enacted, Section 15 of the Environment (Protection) Act made contravention punishable with imprisonment up to five years, or a fine up to Rs 1 lakh, or both, with an additional daily fine and up to seven years where the failure continued beyond a year after conviction. The Jan Vishwas (Amendment of Provisions) Act, 2023 substituted a civil scheme: penalties from Rs 10,000 to Rs 15 lakh, determined by adjudicating officers appointed under the Act, with an appeal to the National Green Tribunal and the proceeds credited to an Environmental Protection Fund. The substituted scheme drew judicial criticism at its birth, the Supreme Court observing in October 2024, in the M. C. Mehta proceedings, that Section 15 had been rendered toothless while the adjudicating machinery remained unappointed, upon which the Union assured the Court the officers would be in place within weeks. Alongside the penalty, directions under Section 5 and environmental compensation levied by the Tribunal remain the heavier practical sanctions.

Q: Do the Solid Waste Management Rules apply to villages and rural areas?

Not directly. Rule 2 applies the rules to urban local bodies and to the urbanising belt around them, outgrowths in urban agglomerations, census towns, notified areas and notified industrial townships, together with the listed institutional territories. A village governed by a gram panchayat under a State panchayat Act lies outside the rulebook’s local authority, and rural sanitation is administered through the rural arm of the national sanitation programme and State panchayat legislation, which cast sanitation among the panchayat’s functions without the rulebook’s apparatus of authorisations, facilities and annual reporting. The boundary is functional rather than clean on the ground: the census town and the outgrowth, rural in governance but urban in density and waste generation, are brought inside the rules precisely because their waste problem is a town’s problem, and a settlement on its way to becoming urban may find the duties arriving before the municipality does.

Q: What must a State government do under the Solid Waste Management Rules?

Rule 11 places the State’s duties on the secretary in charge of urban development. Within one year of the rules’ notification, the State had to prepare a State policy and strategy on solid waste management in consultation with stakeholders including the waste pickers’ representatives, setting incentives, a strategy and a plan. The secretary must ensure the identification and allocation of suitable land to local bodies for processing and disposal facilities, and the development of regional facilities on public private partnership lines among groups of cities. The State secretary for industries must facilitate the market for city compost and its co-marketing with chemical fertilisers and ease loans for plant construction. The State must also frame a scheme for registering waste pickers and waste dealers, constitute the State Level Advisory Body under Rule 23 to review implementation at least once in six months, notify buffer zones around facilities, and meet its share of the funding the plans require.