India’s Battery EPR Market Has Split in Two: Lead Has 8.49 Lakh Tonnes of Credits Available. Lithium Has Just 188 Tonnes.

At first glance, the Central Pollution Control Board’s battery dashboard looks reassuring. It lists 5,312 registered producers and 591 registered recyclers. Certificate transfer is operational. Lakhs of tonnes of credits have been generated and moved through the system.

Then the metals are separated.

For lead, registered recyclers had generated 24.54 lakh tonnes of EPR credits. After transfers to producers, 8.49 lakh tonnes remained available.

For lithium, the same dashboard showed 843.557 tonnes generated, 655.482 tonnes transferred and only 188.075 tonnes available. The lithium-linked producer target displayed on the portal was 92,364.886 tonnes.

Those figures do not mean India is missing 92,000 tonnes of waste lithium-ion batteries. CPCB measures these certificates in recovered key battery metal, not in the weight of whole batteries. Nor does the dashboard prove that producers have defaulted. It does not publicly show the financial-year vintage, due-date split or last-updated time behind the aggregated target.

What it does show is important enough: lead and lithium are operating as two very different EPR markets under the same rulebook.

The numbers at a glance

The dashboard quantities are metal-specific EPR certificate tonnes. They are not tonnes of complete waste batteries.

One rulebook is producing two certificate markets

Battery EPR is often discussed as if one certificate can satisfy any battery obligation. CPCB’s mechanism is more exact.

A producer’s target depends on the battery category, chemistry, quantity placed in the market, metal composition and the applicable recovery factor. A recycler’s certificate is also metal-specific. Lead-acid recycling produces lead certificates. Lithium-ion recycling can produce certificates linked to lithium, nickel, manganese, cobalt, aluminium, iron and copper.

That distinction changes the commercial question. A producer cannot assume that a large national inventory of battery credits means its own obligation is easy to cover. The required certificate has to match the relevant battery chemistry and key metal.

On the 29 October dashboard snapshot, lead credit generation was equal to about 93.28% of the displayed lead target. Lithium credit generation was equal to about 0.91% of the displayed lithium target.

(This is our own estimate, calculated by dividing CPCB’s displayed credits generated by its displayed producer target for each metal.)

The contrast does not establish a violation. It establishes a difference in market depth. Lead has a mature scrap flow, a long-established secondary-smelting industry and a large visible credit inventory. Lithium has a much younger end-of-life stream, several chemistries and far fewer visible credits measured against the target shown on the portal.

For an EPR team, that means “battery-compliant” is too broad a description. Compliance has to be mapped metal by metal.

A lithium certificate begins after recovered metal is sold

The 188-tonne figure becomes clearer when the certificate mechanism is followed from scrap to portal.

CPCB ties each certificate to the quantity of an identified battery metal that a recycler recovers and subsequently sells. The recycler reports the batteries procured, the quantity processed, the individual metals recovered and the sales invoices for those metals. The corresponding quantity is then reflected in the recycler’s certificate wallet.

In simple terms, collecting a battery is not enough. Shredding it is not enough. Producing black mass is not automatically the same as generating a lithium certificate. The portal mechanism is tied to the recovered key metal produced and sold, with supporting commercial records.

This matters because lithium-ion recycling is a chain, not a single operation. One unit may discharge and dismantle battery packs. Another may shred cells and produce black mass. A further refining stage may recover lithium, cobalt, nickel or manganese compounds. Each stage can be commercially valuable, but the EPR certificate system ultimately asks what key metal emerged, in what quantity, and whether its sale can be evidenced.

Lead-acid batteries have a simpler certificate identity. Their key metal is lead. Lithium-ion batteries can carry very different metal profiles depending on chemistry. Lithium iron phosphate batteries contain no nickel or cobalt in the cathode chemistry. Nickel manganese cobalt batteries do. Lithium cobalt oxide batteries have another composition again.

This is why nameplate recycling capacity cannot be treated as certificate supply. A plant may be able to receive battery scrap, but certificate liquidity depends on actual feedstock, recovery, sale and portal-grade documentation for the relevant metal.

The dashboard signals scarcity, but it is not a default list

The most tempting calculation is also the one that needs the greatest care.

CPCB displayed a lithium-linked target of 92,364.886 tonnes and 655.482 tonnes of credits procured. The difference is 91,709.404 tonnes. The 188.075 tonnes shown as available equal about 0.21% of that difference.

(This is our own estimate from the figures displayed on CPCB’s National Dashboard on 29 October 2026. It is a comparison of public aggregates, not a finding of overdue non-compliance.)

For lead, the comparable difference between the displayed target and procured credits was 10.26 lakh tonnes. The 8.49 lakh tonnes of available lead credits would equal about 82.76% of that difference.

(This is our own estimate using the same method. CPCB does not label the dashboard target by financial-year vintage, so the result should not be read as a settlement calculation.)

Three missing pieces prevent a stronger legal conclusion.

First, the dashboard does not say whether the target is cumulative across financial years or limited to one compliance period. Second, it does not separate obligations already due from those that may fall due later. Third, it does not publish a visible update timestamp beside the table.

Until CPCB clarifies those points, it would be wrong to call the entire displayed difference a producer default. But it would also be wrong to ignore the market signal. The lithium credits visible as available are extremely small beside the lithium-linked target displayed on the same official page.

For brands, this is a procurement warning. For recyclers, it is evidence that recovered lithium supported by clean records can occupy a scarce part of the certificate market. For regulators, it is a reason to make the dashboard’s time period and certificate vintage clearer.

Lithium cannot simply copy the lead market

India’s lead scrap chain has been built over decades. The lithium-ion stream is still waiting for much of its future feedstock to reach end of life.

NITI Aayog’s 2026 circular-economy report estimated that India would have about 36,000 tonnes of end-of-life lithium-ion batteries in 2025. Consumer electronics were expected to contribute 33,120 tonnes, while electric vehicles contributed 1,080 tonnes and energy-storage systems 1,800 tonnes. The report estimated only 5,040 tonnes moving through formal channels, with 18,000 tonnes handled informally and about 12,600 tonnes remaining uncollected.

That is the structural problem behind the certificate table. Producers can place large volumes of batteries into the market long before those batteries return as formal, traceable scrap. EV batteries can remain in service for years. Some packs may later be repaired, repurposed or refurbished before recycling. Yet CPCB’s public registration table showed only two refurbisher registrations issued on 29 October 2026.

Feedstock also has to reach the right kind of plant. CPCB’s July 2026 recycling guidelines distinguish lithium-ion operations by processing stage. The chain can include dismantling, black-mass production and deeper recovery of metal salts or metals. Adding capacity at one stage does not guarantee adequate recovery at the next.

Chemistry adds another layer. A recycler buying mixed lithium-ion scrap does not receive a uniform basket of value. An LFP pack, an NMC pack and a phone battery create different recovery economics and different potential certificate outputs. A purchase contract written only in tonnes of “lithium battery scrap” can hide the detail that decides both recovery value and EPR-credit value.

The businesses that solve identification, safe collection, chemistry segregation and documented downstream recovery will do more than move scrap. They will create the evidence on which scarce certificates depend.

The price band cannot manufacture supply

India has already tried to stop battery EPR certificates from trading at arbitrary prices.

The Battery Waste Management Amendment Rules, 2024 require CPCB to set the minimum certificate price at 30% of the applicable environmental compensation and the maximum at 100%. CPCB’s environmental-compensation guidelines list the lithium certificate range at ₹720 to ₹2,400 per kilogram of recovered lithium.

That is a regulatory price band, not a quoted market price and not a promise that a buyer can obtain unlimited credits inside the range. A ceiling can limit the price paid for an available certificate. It cannot produce more recovered lithium, bring an old battery into the formal system or correct a missing sales invoice.

This distinction matters for procurement. If a producer waits until the filing cycle to discover that the correct metal-specific credit is thinly supplied, a permitted price range does not solve the timing problem. Long-term collection and recovery arrangements may matter more than a last-minute search for certificates.

It also matters for recyclers. The opportunity is not simply to generate more certificates. It is to generate certificates that survive reconciliation. Waste procurement records, processing quantities, recovery yields, GST-linked sales evidence and portal entries must tell the same story.

EPR credits and recycled content are separate tests

The next pressure point is already written into the rules.

Buying an EPR certificate helps a producer meet its waste-management obligation. Using domestically recycled material in a new battery is a separate requirement. The same recovered material may support both parts of a circular supply chain, but the obligations should not be treated as interchangeable paperwork.

The Gazette schedule requires portable and EV batteries to contain at least 5% recycled material by total dry weight in FY 2027-28. The requirement rises to 10% in FY 2028-29, 15% in FY 2029-30 and 20% from FY 2030-31.

Automotive and industrial batteries are on an earlier schedule. Their minimum was 35% in FY 2024-25 and FY 2025-26, and it is 40% in FY 2026-27 and thereafter.

Lead’s established recycling base makes that earlier schedule easier to understand. Lithium producers face a different test from 1 April 2027: they will need verifiable recycled material for new portable and EV batteries while the public dashboard already shows a very shallow pool of lithium EPR credits.

The credit market and the recycled-material market are not identical, but both depend on the same physical chain performing properly. Batteries must be collected, identified, processed and refined. Recovered output must meet the buyer’s specification. The paperwork must prove where it came from and where it went.

This is where EPR stops being an annual filing exercise and becomes supply-chain design.

What this means for you

Brands and EPR producers: Break the obligation down by battery category, chemistry and key metal. Do not use total battery-credit inventory as a proxy for availability. Keep EPR-certificate procurement separate from recycled-content sourcing, then connect both plans to the same verified recovery partners.

Battery recyclers and refiners: Measure the value of an output twice. First, ask what the recovered material can earn in the physical market. Second, ask whether its production and sale create a valid metal-specific certificate. Capacity without feedstock will not generate credits, and recovery without reconciled sales evidence may not create usable portal value.

Aggregators and collection partners serving brands: Chemistry information and chain-of-custody records are becoming commercial assets. A traceable lot that reaches the correct registered recycler can support a more valuable compliance outcome than an unidentified mixed load.

Companies importing batteries or equipment containing batteries: Registration and targets attach to the producer definition, which includes importers. Map the battery inside the product, its chemistry and its applicable target before the compliance period closes. Import documentation, sales data and EPR records should reconcile.

What to watch

1. 30 November 2026: CPCB has extended the deadline for filing FY 2025-26 annual returns to this date. Watch whether updated filings materially change the dashboard’s metal-wise targets or procured-credit totals.
2. CPCB’s dashboard methodology: A published reporting vintage, last-updated timestamp and split between due and future obligations would allow the market to distinguish a compliance shortfall from a cumulative pipeline.
3. 1 April 2027: The FY 2027-28 recycled-content requirement begins at 5% for portable and EV batteries. Demand for verified domestically recycled material will then sit beside the existing demand for EPR certificates.
4. Formal lithium collection: The most important supply signal will not be another plant announcement. It will be evidence that more end-of-life batteries are moving from informal or uncollected channels into registered, chemistry-aware recovery chains.

The bottom line

India does not have a single battery EPR market. It has a mature lead market with a large visible credit inventory and a lithium market with only 188.075 tonnes shown as available against a much larger displayed target. Brands that plan by metal, contract for traceable recovery and separate certificate compliance from recycled-content sourcing will be better prepared than those treating battery EPR as one annual purchase.