uogent®Analysis / Chemicals and Industrial Infrastructure
What makes a chemical park work
How shared services help chemical manufacturers operate reliably

A chemical park earns its value when a manufacturer can start production on schedule and continue operating with dependable utilities, predictable service costs and a workable route for every waste stream. Land, roads and equipment support that operating promise. A park proposal should therefore cover how shared services will be delivered, paid for and restored if or when something fails.
The Union Cabinet approved BHAVYA Rasayan on 24 July 2026, with a central outlay of ₹3,030 crore for 2026–27 to 2030–31, including ₹30 crore for administration. The scheme supports three new chemical parks, with central assistance of up to ₹1,000 crore per park and a minimum state contribution of ₹500 crore. [1] [3]
As of 19 October 2026, the Department of Chemicals and Petrochemicals is inviting state proposals by 30 November 2026. [2] A strong proposal will connect the needs of the manufacturers moving in with the services the park can deliver. It will also explain how the operator will pay for those services over time. That is the focus of this article.
Choose a location that can deliver
Location carries half the marks in the published selection framework: 24 for land, six for proximity to the coast and 20 for transport links. Incentives, power charges and skills institutions account for 25 more; a broader assessment receives the remaining 25. The scheme is for new developments and requires at least eight square kilometres of adjoining land free of legal claims or charges that restrict its use. [3]
Figure 1
BHAVYA Rasayan selection criteria
Maximum marks out of 100 · published scheme guidelines · verified 19 October 2026
Land availability receives 24 marks, coastal proximity 6, transport connectivity 20, state incentives 15, power charges 5, skills institutions 5 and qualitative assessment 25. Total 100.
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| criterion | maximum_marks | assessment | source_pages | evidence_type | denominator_marks |
|---|---|---|---|---|---|
| Land availability | 24 | Quantitative | 16–17 | Official selection framework | 100 |
| Coastal proximity | 6 | Quantitative | 16–17 | Official selection framework | 100 |
| Transport connectivity | 20 | Quantitative | 16–17 | Official selection framework | 100 |
| State incentives | 15 | Quantitative | 16–17 | Official selection framework | 100 |
| Power charges | 5 | Quantitative | 16–17 | Official selection framework | 100 |
| Skills institutions | 5 | Quantitative | 16–17 | Official selection framework | 100 |
| Qualitative assessment | 25 | Qualitative | 16–17 | Official selection framework | 100 |
A good location is a starting point. A nearby port must be able and permitted to handle the park’s chemicals. A water source must provide dependable supply through the dry season. For each connection, the proposal should name the provider, the capacity available, the completion date and how performance will be checked.
Alongside the selection score, Quogent recommends a practical operating plan. Separate confirmed customer commitments from expressions of interest. Show which shared facilities are needed first, what they will cost to run while demand is still low, and what happens if a service fails.
Plan around the manufacturers moving in
A factory that blends finished ingredients can need very different services from one that makes chemicals through reactions. Raw materials, storage, steam and wastewater treatment all vary. Planning should start with what each factory will make, what it will consume and what waste it will produce.
India’s Petroleum, Chemicals and Petrochemicals Investment Regions, or PCPIRs, show how different industrial areas can be. The Department’s 2025–26 annual report remains its latest annual report at this review date. Its figures below provide historical context, rather than a count of investment or factories as of October 2026. [4]
Regional context from the DCPC Annual Report 2025–26
PCPIR region | Investment reported | Chemical units |
|---|---|---|
Dahej, Gujarat | 1,28,509 | 2,079 |
Visakhapatnam–Kakinada, Andhra Pradesh | 68,148 | 154 |
Paradeep, Odisha | 1,43,881 | 13 |
Source: DCPC Annual Report 2025–26, printed page 7. These are published regional aggregates with different industrial mixes and histories, not an October 2026 snapshot. The report does not specify a uniform observation date.
Investment and factory count tell different stories. A few large plants may need different shared services from hundreds of smaller manufacturers. These figures describe large regions with different histories; they do not rank individual parks. They also lack a common observation date and information on service reliability.
Ask prospective tenants when they will start production, how quickly output will grow, and how much water, power, steam, storage and waste treatment they will need. This makes it easier to decide what to share. Equipment serving one large customer may need different ownership and pricing from a fire station serving the whole park.
Exchanges between factories need the same care. One firm’s by-product can supply another only if its quality and delivery schedule suit the buyer. Agreements should cover testing, price, responsibility when quality falls short, and backup supply or disposal during shutdowns.
Plan for the cost of running shared services
A grant can help build shared facilities. Staffing, power, maintenance, treatment chemicals and waste disposal still need to be paid for every year. Early customers can face high charges because there are fewer users to share these costs. The financial plan should allow for this period.
The Department’s October brochure makes the state’s contribution clearer: it must also provide land at its own cost and build external infrastructure up to the park. The scheme guidelines assign operation and management of shared assets to the state implementing agency; the central government does not take on their operating liabilities. [3] Those responsibilities belong in the budget and service contracts from the start.
Consider a treatment facility able to handle 20,000 cubic metres a day. Assume it operates 365 days a year, with fixed running costs of ₹12 crore a year and a further ₹15 for each cubic metre treated. Fixed costs stay the same across this example; variable costs increase with the amount treated. These are illustrative assumptions, not a quoted tariff. Utilisation means the share of available capacity actually used.
Figure 2
Shared utility operating cost by utilisation
Illustrative scenario · ₹ per m³ treated · constant annual fixed cost and unit variable cost
Illustrative operating cost is ₹80.75 per cubic metre at 25% utilisation, ₹47.88 at 50%, ₹36.92 at 75% and ₹31.44 at 100%. These are scenario outputs, not observed tariffs.
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| utilisation | cost_rs_m3 | component | evidence_type | annual_flow_m3 | total_cost_rs_m3 | variable_cost_rs_m3 | annual_fixed_cost_rs | design_capacity_m3_day |
|---|---|---|---|---|---|---|---|---|
| 25% utilisation | 65.7534 | Fixed operating cost | Illustrative calculation, not a tariff benchmark | 1825000 | 80.7534 | 15 | 120000000 | 20000 |
| 25% utilisation | 15 | Variable operating cost | Illustrative calculation, not a tariff benchmark | 1825000 | 80.7534 | 15 | 120000000 | 20000 |
| 50% utilisation | 32.8767 | Fixed operating cost | Illustrative calculation, not a tariff benchmark | 3650000 | 47.8767 | 15 | 120000000 | 20000 |
| 50% utilisation | 15 | Variable operating cost | Illustrative calculation, not a tariff benchmark | 3650000 | 47.8767 | 15 | 120000000 | 20000 |
| 75% utilisation | 21.9178 | Fixed operating cost | Illustrative calculation, not a tariff benchmark | 5475000 | 36.9178 | 15 | 120000000 | 20000 |
| 75% utilisation | 15 | Variable operating cost | Illustrative calculation, not a tariff benchmark | 5475000 | 36.9178 | 15 | 120000000 | 20000 |
| 100% utilisation | 16.4384 | Fixed operating cost | Illustrative calculation, not a tariff benchmark | 7300000 | 31.4384 | 15 | 120000000 | 20000 |
| 100% utilisation | 15 | Variable operating cost | Illustrative calculation, not a tariff benchmark | 7300000 | 31.4384 | 15 | 120000000 | 20000 |
At 25% utilisation, annual volume is 20,000 × 365 × 0.25 = 1,825,000 m³. Spreading ₹12 crore across that volume and adding ₹15 gives about ₹80.75 per m³. At full use, the cost falls to ₹31.44. The example excludes construction repayment, financing, taxes, major renewals and profit. Actual costs will also depend on how the plant performs at lower volumes.
Pricing should explain what customers pay to reserve capacity and what they pay for actual use. Wastewater charges may also need to reflect how much pollution a factory sends. Set out how prices can change, how maintenance is funded, and who covers the shortfall if customers arrive late or fail to pay.
Know what wastewater the park can treat
A common effluent treatment plant, or CETP, treats wastewater from several factories. Its stated capacity usually describes how much water it can receive. Its ability to treat that water also depends on the pollutants present, their concentration, salt content and toxicity. The Central Pollution Control Board highlights poor control of factory discharges, weak monitoring, inadequate separation of waste streams and shortages of technical staff as recurring problems. [5]
Figure 3 shows chemical oxygen demand, or COD, in water entering and leaving 12 listed treatment plants. COD measures the oxygen needed to chemically oxidise material in the water; it is one indicator of pollution, not a complete water-quality test. These are all entries in the Maharashtra Pollution Control Board’s main table with sample dates within 90 days of 19 October 2026. [6] The table covers several industrial sectors, including textiles, so it is not a representative sample of India’s chemical parks.
Figure 3
Reported inlet and outlet COD concentrations
MPCB public table · all 12 listed plants with samples aged 0–90 days on 19 October 2026 · mg/L
Twelve recent table entries show inlet COD from 276 to 3,640 mg/L and outlet COD from 68 to 688 mg/L. L.K. Akiwate is the one pair with a higher outlet value (688) than inlet value (352). Values do not establish treatment efficiency or compliance.
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| plant | cod_mg_l | stream | as_of | age_days | source_url | sample_date | evidence_type | plant_full_name | design_capacity_mld |
|---|---|---|---|---|---|---|---|---|---|
| Butibori | 696 | Inlet | 2026-10-19 | 34 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-09-15 | Reported sample concentration | Butibori CETP Pvt. Ltd., Dist. Nagpur | 5 |
| Butibori | 68 | Outlet | 2026-10-19 | 34 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-09-15 | Reported sample concentration | Butibori CETP Pvt. Ltd., Dist. Nagpur | 5 |
| Ichalkaranji 1 MLD | 3640 | Inlet | 2026-10-19 | 14 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-05 | Reported sample concentration | Ichalkaranji Textile Development Cluster Ltd. (1 MLD), Dist. Kolhapur | 1 |
| Ichalkaranji 1 MLD | 236 | Outlet | 2026-10-19 | 14 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-05 | Reported sample concentration | Ichalkaranji Textile Development Cluster Ltd. (1 MLD), Dist. Kolhapur | 1 |
| Ichalkaranji 12 MLD | 2000 | Inlet | 2026-10-19 | 14 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-05 | Reported sample concentration | Ichalkaranji Textile Development Cluster Ltd. (12 MLD), Dist. Kolhapur | 12 |
| Ichalkaranji 12 MLD | 156 | Outlet | 2026-10-19 | 14 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-05 | Reported sample concentration | Ichalkaranji Textile Development Cluster Ltd. (12 MLD), Dist. Kolhapur | 12 |
| Kagal Hatkanangale | 296 | Inlet | 2026-10-19 | 14 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-05 | Reported sample concentration | Kagal-Hatkanangale C.E.T.P.,, Dist. Kolhapur | 10 |
| Kagal Hatkanangale | 272 | Outlet | 2026-10-19 | 14 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-05 | Reported sample concentration | Kagal-Hatkanangale C.E.T.P.,, Dist. Kolhapur | 10 |
| L.K. Akiwate | 352 | Inlet | 2026-10-19 | 49 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-31 | Reported sample concentration | L.K. Akiwate Industrial Co Op, Estate Ltd, Dist. Kolhapur | 0.8 |
| L.K. Akiwate | 688 | Outlet | 2026-10-19 | 49 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-31 | Reported sample concentration | L.K. Akiwate Industrial Co Op, Estate Ltd, Dist. Kolhapur | 0.8 |
| Kurkumbh | 2618.4 | Inlet | 2026-10-19 | 41 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-09-08 | Reported sample concentration | Kurkumbh Environment Protection Co op Society, Dist. Pune | 1 |
| Kurkumbh | 192.8 | Outlet | 2026-10-19 | 41 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-09-08 | Reported sample concentration | Kurkumbh Environment Protection Co op Society, Dist. Pune | 1 |
| MMA CETP | 320 | Inlet | 2026-10-19 | 12 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-07 | Reported sample concentration | MMA-CETP Co Operative Society Ltd., Dist. Raigad | 7.5 |
| MMA CETP | 152 | Outlet | 2026-10-19 | 12 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-10-07 | Reported sample concentration | MMA-CETP Co Operative Society Ltd., Dist. Raigad | 7.5 |
| RIA CETP | 720 | Inlet | 2026-10-19 | 77 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-03 | Reported sample concentration | RIA CETP Co-op. Society Ltd., Dist. Raigad | 10 |
| RIA CETP | 204 | Outlet | 2026-10-19 | 77 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-03 | Reported sample concentration | RIA CETP Co-op. Society Ltd., Dist. Raigad | 10 |
| PRIA CETP | 276 | Inlet | 2026-10-19 | 84 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-07-27 | Reported sample concentration | PRIA CETP (I) Ltd., Dist. Raigad | 15 |
| PRIA CETP | 220 | Outlet | 2026-10-19 | 84 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-07-27 | Reported sample concentration | PRIA CETP (I) Ltd., Dist. Raigad | 15 |
| Thane–Belapur | 316 | Inlet | 2026-10-19 | 49 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-31 | Reported sample concentration | Thane-Belapur Association, Dist. Thane | 27 |
| Thane–Belapur | 208 | Outlet | 2026-10-19 | 49 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-31 | Reported sample concentration | Thane-Belapur Association, Dist. Thane | 27 |
| Badlapur | 1616 | Inlet | 2026-10-19 | 70 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-10 | Reported sample concentration | Badlapur CETP Association, Dist. Thane | 8 |
| Badlapur | 316 | Outlet | 2026-10-19 | 70 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-10 | Reported sample concentration | Badlapur CETP Association, Dist. Thane | 8 |
| ACMA CETP | 816 | Inlet | 2026-10-19 | 56 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-24 | Reported sample concentration | ACMA - CETP-Co-operative Society Ltd, Dist. Thane | 0.25 |
| ACMA CETP | 160 | Outlet | 2026-10-19 | 56 | https://www.mpcb.gov.in/cetp-reports-at-glance | 2026-08-24 | Reported sample concentration | ACMA - CETP-Co-operative Society Ltd, Dist. Thane | 0.25 |
Read these pairs with care. They come from different plants and dates, and the table does not show whether the incoming and outgoing samples represent the same water moving through treatment. It also lacks actual flow data. The pairs cannot establish treatment efficiency, compliance or a ranking. One pair, for L.K. Akiwate, shows a higher outlet value than inlet value. That is a reason to check the sampling context, not to infer the cause from this table alone.
Each factory therefore needs clear conditions for what it may discharge, backed by meters, sampling and a response when those conditions are breached. Wastewater requiring specialist treatment should be kept separate until it can safely enter the shared plant.
Measure pollution as well as water volume
Less wastewater does not always mean less treatment work. A smaller volume can carry more pollution if it is more concentrated. The calculation below combines volume and concentration. Dividing by 1,000 converts the result to kilograms per day when these units are used. Here, flow is the water received each day, measured in cubic metres (m³), and COD concentration is measured in milligrams per litre (mg/L).
For a plant designed to receive 10,000 m³ a day at 1,000 mg/L COD, the design load is 10,000 kg a day. At 8,000 m³ a day and 2,000 mg/L, the load rises to 16,000 kg a day. Water volume is at 80% of design, while COD load is at 160%. Figure 4 compares these two measures in four scenarios; each bar shows the share of that measure’s design load. These are illustrative calculations, not treatment limits.
Figure 4
Water volume and pollution load in four scenarios
Illustrative calculation · percentage of a defined design basis · 100% equals design load
High COD (concentrated inflow) uses 80% of design water volume but 160% of design COD load. Design values are 100% for both. Low flow is 50% for both and high flow 120% for both.
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| scenario | design_load_pct | metric | flow_m3_day | evidence_type | inlet_cod_mg_l | cod_load_kg_day | scenario_detail | design_flow_m3_day | design_cod_load_kg_day |
|---|---|---|---|---|---|---|---|---|---|
| Low flow | 50 | Water volume | 5000 | Illustrative mass balance | 1000 | 5000 | Lower flow | 10000 | 10000 |
| Low flow | 50 | COD load | 5000 | Illustrative mass balance | 1000 | 5000 | Lower flow | 10000 | 10000 |
| Design | 100 | Water volume | 10000 | Illustrative mass balance | 1000 | 10000 | Design basis | 10000 | 10000 |
| Design | 100 | COD load | 10000 | Illustrative mass balance | 1000 | 10000 | Design basis | 10000 | 10000 |
| High COD | 80 | Water volume | 8000 | Illustrative mass balance | 2000 | 16000 | Concentrated | 10000 | 10000 |
| High COD | 160 | COD load | 8000 | Illustrative mass balance | 2000 | 16000 | Concentrated | 10000 | 10000 |
| High flow | 120 | Water volume | 12000 | Illustrative mass balance | 1000 | 12000 | Higher flow | 10000 | 10000 |
| High flow | 120 | COD load | 12000 | Illustrative mass balance | 1000 | 12000 | Higher flow | 10000 | 10000 |
Apply this percentage calculation to water volume or COD load separately, using matching units. Expansion decisions should consider both measures and the pollutants involved. Some factories may need to treat their wastewater before sending it to the common plant. The operator also needs a way to trace unusual discharges and hold them safely. Two streams with the same COD may still require different treatment.
Water reuse needs clear records too. Report freshwater drawn, reused water supplied and water leaving the site, including in products, waste or evaporation. Do not count the same recycled water as a fresh supply on each trip around the system. Reuse targets must fit the quality needed and the treatment available.
Prepare shared services for disruption
Shared facilities can reduce duplication, but an outage can affect many factories at once. If a common steam pipe, water main or treatment system fails, the operator needs to isolate the problem, help factories shut down safely and restore service in an agreed order.
Jurong Island shows what coordinated infrastructure can support. JTC describes more than 100 energy and chemical companies linked by over 100 kilometres of pipelines, with shared utilities and service corridors. [7] The useful lesson is coordination. Each Indian park will need arrangements suited to its own manufacturers, raw materials, climate and regulation.
Service contracts should make promises specific: water pressure and quality, electricity reliability, wastewater acceptance conditions and repair times. Customers need to know what the quoted price includes and who bears the cost when delivery falls short.
Transport and storage must suit the chemicals being handled. Check tank capacity, safe loading, spill containment and emergency access, as well as the full route to the port. Shared laboratories, maintenance teams and emergency services deserve the same attention as physical connections.
Responsibilities for approvals must also be clear. The 28 January 2026 CETP reform removes the separate prior environmental-clearance requirement for CETPs under the environmental impact assessment notification, while retaining consents to establish and operate from the state pollution-control authority. Environmental safeguards are enforced through those consents; the Ministry’s explanation includes closed pipelines and continuous online monitoring. [8] This does not exempt the wider park or its factories from their own approval requirements. Identify the requirements for each separately.
Give the operator information it can act on
The park operator needs clear authority to approve connections, enforce service terms, plan maintenance, resolve bills and coordinate emergencies. These responsibilities should be written down, while keeping the operator’s role separate from the regulator’s legal powers.
Information needs a date as well as a value. In the MPCB table retrieved on 19 October 2026, 12 of the 25 displayed samples were no more than 90 days old; two were over a year old. [6] This describes the age of the readings visible to the public, not how frequently each plant is sampled. An older entry does not prove that later sampling or regulatory work has stopped.
Figure 5
Age of the latest sample shown for each CETP
MPCB public table · 25 listed plants · days from reported sample date to 19 October 2026
Of 25 public-table entries, 12 have samples aged 0–90 days, 7 aged 91–180 days, 4 aged 181–365 days and 2 over 365 days. These counts describe public data recency, not sampling frequency or treatment performance.
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| sample_age_band | plants | as_of | evidence_type | all_listed_plants |
|---|---|---|---|---|
| 0–90 days | 12 | 2026-10-19 | Derived from reported sample dates | 25 |
| 91–180 days | 7 | 2026-10-19 | Derived from reported sample dates | 25 |
| 181–365 days | 4 | 2026-10-19 | Derived from reported sample dates | 25 |
| Over 365 days | 2 | 2026-10-19 | Derived from reported sample dates | 25 |
Internally, the operator needs factory-level records of water volumes, pollutant loads, outages, maintenance and payments. Public reports can show overall results while protecting commercial information. Missing or old readings should be clearly labelled.
Use those records to prompt action. Investigate rising pollution loads, fix repeated steam interruptions and address overdue bills before services run short of funds. Give each issue a responsible person, an agreed response and a deadline.
Expand when demand supports it
Start with the services the first group of customers will actually need. Reserve space and connections for expansion, but size the initial facilities around credible demand. This helps avoid paying to maintain expensive equipment long before enough customers arrive.
Before construction, line up customer schedules, service contracts, finance, approvals and ownership of shared assets. Before accepting wastewater, test treatment with representative inputs and rehearse the response to an unsuitable discharge or equipment failure. Use the first year’s operating records to guide expansion.
The following questions can guide regular reviews. Targets should reflect the site’s engineering, contracts and permissions.
Operating questions and measures to publish
Operating question | Measure to publish |
|---|---|
Can factories rely on shared services? | Hours of interruption; quality problems; time taken to restore service. |
Can treatment keep up with production? | Water volume and pollutant load against design; treated-water quality; where remaining waste goes. |
Can shared facilities pay their running costs? | Capacity in use; costs covered by revenue; unpaid bills; money reserved for maintenance. |
Can the park handle disruption? | Backup services available; findings from emergency exercises; problems still unresolved. |
Are customers moving into production? | Start dates against commitments; factories operating; repeat orders and expansion. |
Is the information current and complete? | Sample dates; reporting delays; missing data; independent checks. |
Proposed Quogent operating checklist. Set targets for the specific site and its service commitments.
For states preparing proposals, the priority is a clear delivery plan: who will use the park, what services they need, what those services will cost and who is responsible for providing them.
A successful chemical park gives manufacturers confidence that shared services will work throughout production. Reliable supply, controlled waste, affordable upkeep and customers choosing to expand are useful signs that the park is delivering.
Sources and methodology
Context and sources were reviewed on 19 October 2026. Figures 2 and 4 are worked examples using stated assumptions, not measurements of existing parks or current tariff quotes. Figure 1 uses the published selection framework; Figures 3 and 5 use the MPCB public-table snapshot described below. Underlying values are available through “View source data” beneath each chart. The regional table retains its annual-report reference period. The recommendations are Quogent’s analysis.
[1] Press Information Bureau. Cabinet approval of BHAVYA Rasayan, 24 July 2026. Open source
[2] Department of Chemicals and Petrochemicals. BHAVYA Rasayan scheme page. The proposal deadline remained 30 November 2026 when checked on 19 October 2026. Open source
[3] Department of Chemicals and Petrochemicals. BHAVYA Rasayan Scheme Guidelines: scope and eligibility, printed pages 5–6; operating and financial responsibilities, section 15; selection weights, Appendix 1, printed pages 16–17. Scheme guidelines · Scheme brochure, released 5 October 2026 (funding responsibilities, page 2).
[4] Department of Chemicals and Petrochemicals. Annual Report 2025–26, the latest annual report listed as of this review. Comparative status of three PCPIRs: printed page 7, PDF page 9. The figures are regional aggregates, lack a uniform observation date and are not a matched performance comparison. Open source
[5] Central Pollution Control Board. Division-wise fact sheet, page 127, supplementary information on CETPs. This background document is used for technical operating constraints, not as a current statement of legal requirements. Open source
[6] Maharashtra Pollution Control Board. CETP Reports at Glance, retrieved 19 October 2026; the page’s latest-reports banner read “19-10-2026 13:31”. Figure 5 includes all 25 main-table entries and excludes the four separately listed proposed or non-functional entries. Age is the number of calendar days from the displayed sample date to 19 October 2026. Figure 3 includes all 12 main-table entries within 0–90 days, an inclusive eligibility window of 21 July–19 October 2026. This is a dated public-table snapshot; sectors, plants and sample dates differ. Open source
[7] JTC. How Jurong Island’s integrated ecosystem drives its sustainable transformation. Used as an institutional example, not a causal estimate of cost savings. Open source
[8] Ministry of Environment, Forest and Climate Change. Notification S.O. 389(E), 28 January 2026, removes item 7(h) from the EIA schedule. Read alongside the Ministry’s explanation of the consent mechanism and environmental safeguards. Gazette notification · Ministry / PIB explanation