Panipat Recycles the World's Clothes but Not Its Pollution, Contends Ground Report

Panipat's formal compliance architecture is more substantial than its environmental outcomes suggest. The cluster's recycling scope extends beyond cotton and wool: it also processes more than 54,000 metric tonnes of PET fibre annually into yarn for carpets, blankets, and fillings—a nascent but growing segment valued at INR 500–600 crore—yet governance systems have not kept pace with even this secondary stream. Industrial units engaged in dyeing, washing, and finishing are required to obtain Consent to Operate from the Haryana State Pollution Control Board (HSPCB), contingent on the installation of functional effluent treatment plants. Those located in the cluster's principal processing zone are required to connect to the CETPs that anchor its wastewater management infrastructure. The regulatory framework, on its face, is not absent.

What is absent is consistent follow-through. In-house ETPs exist primarily in medium and largescale units, but their functioning is described in the report as inconsistent. More critically, sludge handling lacks traceability. Sludge generated through dyeing and finishing operations—containing dye residues, salts, and heavy metals—is frequently handed to third-party vendors without documentation of where it goes or how it is ultimately disposed. In some cases, informal disposal has been reported.

The sludge generated across these units alone amounts to an estimated 7,684 tonnes of hazardous ETP chemical sludge per year. Of this, the HSPCB recorded 3,012 tonnes disposed of in secured landfills and 183 tonnes incinerated in a single reporting year. The remaining volume—nearly 4,489 tonnes classified as recyclable or utilisable—enters a disposal chain whose ultimate destinations are, for the most part, unverified.

Solid waste tells a similar story. A large portion of unrecyclable waste and fibre dust—estimated at between 3,000 and 7,200 tonnes per annum—is either dumped on open land or passed to informal waste handlers. Weak segregation at the unit level causes recyclable, non-recyclable, and hazardous materials to be mixed before disposal, compounding the difficulty of any downstream recovery. Informal burning of solid waste has been reported across parts of the cluster, contributing directly to localised air pollution.

The institutional conditions that allow this are well documented in the report. Panipat has no cluster-wide waste management protocol. Units operate independently, without standardised procedures for segregation, collection, or disposal. Tracking mechanisms are largely absent; most units do not maintain waste management records of any kind. Small units—which constitute around 70% of textile enterprises in the cluster—cannot afford individual dust collection systems, whose capital cost is estimated at between INR 5 and 15 lakh. The consequence is that unregulated disposal continues not as deliberate evasion, but as the default outcome of a system without viable alternatives at the small-unit level.

What emerges from this picture is a compliance model that is, in the report's implicit framing, installation-driven rather than outcome-driven. The presence of an ETP satisfies the condition for a Consent to Operate. It does not, in itself, ensure that sludge is handled responsibly, that waste streams are properly segregated, or that the environmental burden generated within the plant boundary is managed beyond it. Infrastructure presence and monitoring integrity are treated, in practice, as the same thing. The evidence suggests they are not.

Coal's exit from Panipat was regulatory rather than voluntary. Following a directive from the Commission for Air Quality Management issued in June 2022, the use of coal and pet coke for industrial heating was banned across the NCR effective January 2023. For a cluster whose dyeing and finishing operations had long depended on coal-fired boilers, the transition was significant. Most industrial units shifted to biomass briquettes or pellets, with around 70% of boilers now running on biomass and 30% on LPG; approximately 20 units made the transition to LPG.

The fuel transition is real. What it has not done is resolve the cluster's combustion-related pollution pressures.

Biomass-fired boilers continue to generate ash and particulate residues as a matter of operational routine. Stack measurements from several units show exceedance of the 80 milligrams per cubic metre suspended particulate matter limit, a norm that was itself tightened from a previous ceiling of 800—a reduction that most enterprises find technically challenging to meet. Outdated fire-tube boilers, running at only 60­65% thermal efficiency, produce elevated carbon monoxide and particulate emissions as a function of their design, regardless of the fuel being burned. The problem, in other words, did not leave with the coal.

Ash and particulate waste generated by the new fuel regime continue to be disposed of informally or mixed with general solid waste. The regulatory directive that drove the fuel transition addressed the source of combustion—the fuel type—without establishing any corresponding framework for managing the residues that combustion produces. Boiler ash, a downstream consequence of both the old and the new energy regime, moves through the same informal disposal channels that handle other solid waste streams in the cluster.

Secondary waste streams compound the picture. Polybags, bale wrappings, and low-grade packaging films used in the transport of imported and domestic textile waste form a growing residue category. These materials are either sold to informal recyclers or disposed of unsafely. Items that are heavily contaminated or unsuitable for mechanical recycling are, in documented cases, burned informally. Unauthorised dumping sites have been reported in parts of the cluster where such materials accumulate.

The air quality consequences are most acute during winter, when biomass combustion intensity rises and atmospheric conditions reduce the dispersal of particulates. The water dimension is equally stark: dyeing operations alone consume between 80 and 120 litres of water per kg of fabric, and total industrial water demand across the cluster runs at an estimated 50 million litres per day. At this point, the cluster's dyeing and finishing operations—which together account for more than 60% of direct Scope 1 emissions—are running at their most polluting, in conditions that amplify rather than dissipate the impact. Advanced emission control systems, including bag filters, electrostatic precipitators, and wet scrubbers, remain largely unadopted across the cluster.

The fuel transition, framed at the time as an environmental intervention, was in important respects exactly that. Removing coal from the energy mix was a meaningful step. But the assumption embedded in the regulatory logic—that changing the fuel source would change the environmental outcome—has proven only partially correct. Combustion residues persist. Informal disposal persists. What changed was the label on the fuel drum, not the system through which its consequences are managed.

The Panipat cluster's sustainability transition is not uniform. It moves at different speeds across different enterprise types, and the distance between those speeds is, in large part, a function of capital. Technologies that require significant upfront investment remain concentrated among larger units with access to finance, export relationships, and compliance infrastructure. For the MSMEs that constitute the overwhelming majority of the cluster—around 6,400 enterprises in total—the economics of high-impact environmental intervention are, in most cases, prohibitive.

The report's technology adoption data makes the stratification visible. Energy already accounts for 20–30% of total production costs across dyeing and spinning units—with some dyeing operations exceeding 30%—leaving little financial headroom for capital investment in clean technologies. Effluent treatment plants have achieved moderate traction, but primarily among larger dyeing units; smaller enterprises without CETP linkage find them financially unviable at the individual unit level. 

Zero Liquid Discharge systems, which would represent the most consequential water-side intervention available to the cluster, are at pilot stage. At an estimated cost of between INR 1.5 and 3 crore per unit, they are described in the report as unaffordable for most MSMEs. A CETP-ZLD hybrid model has been proposed as an alternative, but has not yet moved beyond the conceptual stage.

Water reuse systems, though promising in their documented results, remain mostly experimental. A pilot facilitated by Solidaridad demonstrated that freshwater consumption could be reduced by 80%—a figure that, if replicated at scale, would materially alter the cluster's water intensity. It has not been replicated at scale. The capital requirement of INR 50 to 75 lakh per unit places it beyond the reach of most smaller enterprises without targeted financial support.

At the lower end of the investment spectrum, the adoption gaps are harder to explain on cost grounds alone. Ventilation and dust control systems—whose capital cost the report estimates at between INR 1 and 5 lakh per unit—are described as very low in adoption across the cluster, with their absence directly linked to indoor air quality problems and worker health risks. IE4 and IE6 energy-efficient motors, similarly affordable at INR 3 to 5 lakh per unit, also show very low uptake. The report attributes this primarily to lack of awareness rather than financial constraint, suggesting that the barrier in these cases is informational as much as economic.

Government subsidy schemes exist on paper but have not translated into meaningful uptake. The ADEETI scheme, administered by the Bureau of Energy Efficiency, offers interest subvention for energy efficiency investments but suffers from poor awareness and low utilisation among MSMEs. SIDBI green loan products, offering concessional financing for pre-approved clean technologies, have been accessed by a small number of solar adopters; most enterprises remain unaware of their eligibility. 

The Haryana Textile Policy provides incentives for solar energy, ZLD, and common CETPs, but is described as underutilised due to limited implementation clarity and facilitation on the ground. Across schemes, the pattern is consistent: financial instruments exist, but the connective tissue between their availability and enterprise-level uptake is largely missing.

What results is a dual-speed transition. Larger, export-oriented units invest in certifications, ETPs, and in some cases solar rooftops, driven by buyer requirements and access to finance. Smaller units, operating on thin margins without dedicated environment, health, and safety personnel, remain outside the reach of both regulatory enforcement and subsidy benefit. Growth in the cluster's overall recycling capacity does not, under these conditions, translate automatically into proportional environmental improvement. The gains accrue unevenly, and the pollution burden remains concentrated where investment capacity is lowest.

The Limits of a Transitional Cluster

Panipat's recycling cluster is neither fully non-compliant nor fully sustainable. It occupies an intermediate condition—one in which infrastructure investment and informal disposal, certified exports and untracked sludge, fuel transition and persistent particulate emissions coexist without apparent contradiction. What the diagnostic evidence makes clear is that expansion alone does not close the gap. Without stronger monitoring, traceable residue management, and financing mechanisms that reach the smallest units where pollution is most concentrated, the cluster risks scaling its output without scaling its environmental safeguards—embedding pollution more deeply under the banner of circular growth.