India’s lithium-ion battery recycling market is moving into a very different phase. Until recently, most discussions around the sector focused on future EV battery waste and the opportunity to recover lithium, nickel and cobalt. In 2026, the commercial question has become more practical: Will a new recycling plant actually get enough battery waste, and who will buy the black mass or recovered materials once the plant starts production?
That distinction is important because India’s battery market is expanding rapidly, but recycling capacity, feedstock availability and downstream material demand are not growing at exactly the same speed.
Official data cited by the Ministry of Heavy Industries projects India’s annual lithium-ion battery demand at approximately 40 GWh in 2025, increasing to about 210 GWh by 2030. The same government release reported 3,391 registered lithium-ion battery producers and 43 registered lithium-ion battery recyclers as of December 2025, with around 15,370 tonnes of Li-ion battery waste recycled since the Battery Waste Management Rules were notified.
The long-term opportunity is therefore significant. The near-term investment case, however, depends heavily on feedstock contracts, chemistry mix, recycling depth and offtake planning.
India’s lithium-ion battery demand is being driven by several markets simultaneously. Electric two-wheelers, three-wheelers and passenger vehicles are increasing battery consumption, while renewable energy developers are creating another large demand centre through battery energy storage systems.
The Ministry of New and Renewable Energy, citing the Central Electricity Authority’s National Electricity Plan, estimates that India’s BESS requirement could increase from approximately 34.72 GWh in 2026-27 to 236.22 GWh by 2031-32.
Consumer electronics remain another important source. Mobile phones, laptops, power tools, telecom equipment and industrial electronics already generate smaller lithium-ion cells with relatively short replacement cycles.
For a recycler, therefore, future waste is likely to originate from three increasingly important streams: consumer electronics, electric mobility and stationary energy storage.
The timing of those waste streams is different. A battery sold today does not automatically become recycling feedstock tomorrow. EV and BESS batteries can remain in operation for several years, and some may enter second-life applications before finally reaching a recycling facility.
That time lag is one of the most important factors in a recycling plant feasibility study.
The January 2026 NITI Aayog report provides one of the clearest pictures of this challenge.
It estimates that approximately 36,000 tonnes of lithium-ion batteries would reach end-of-life in 2025, including around 33.12 kT from consumer electronics, 1.08 kT from EVs and 1.8 kT from energy-storage systems. However, the report estimates that around 12.6 kT could remain uncollected, 18 kT could move through informal channels and only about 5.04 kT through formal collection channels.
This changes the investment narrative considerably.
India does not simply have a shortage of recycling machines. NITI Aayog estimates that announced lithium-ion battery processing capacity was already above 80 kT against approximately 15 kT that would need recycling in 2025. By 2030, announced processing capacity could reach approximately 115 kT while actual available end-of-life supply is estimated at around 60 kT.
In other words, the near-term competition may increasingly be for battery waste, not just for customers.
A promoter planning a 5 TPD, 10 TPD or 20 TPD facility should therefore not size the project merely using national EV growth projections. The DPR needs to determine how many tonnes of acceptable battery chemistry can realistically be contracted within the project’s procurement radius.
The longer-term numbers remain compelling.
NITI Aayog estimates that India’s end-of-life lithium-ion battery availability could grow at approximately 26% annually, from around 19 kT in 2023 to approximately 233 kT by 2035. EV and energy-storage batteries are expected to become increasingly important contributors to that waste stream.
This means today’s feedstock constraint should not be interpreted as a weak long-term market.
Instead, it suggests that plants commissioned during the next few years need a business model capable of surviving the transition period before large EV and BESS battery retirement volumes become available.
Manufacturing scrap, consumer-electronics batteries, OEM warranty returns, imported eligible scrap and contractual collection networks can therefore be strategically important during the early years of a project.
The buyer depends primarily on how far downstream the recycler processes the battery.
A plant that stops after mechanical shredding has a very different customer base from one that installs hydrometallurgy and produces battery-grade lithium carbonate or nickel sulphate.
| Recycler output | Typical potential buyer | Normal commercial requirement | Offtake model |
|---|---|---|---|
| Black mass | Hydrometallurgical refiners and critical-mineral processors | Chemistry, Li/Ni/Co content, moisture and impurities | Assay-linked purchase |
| Lithium carbonate / lithium salts | Cathode-material manufacturers, chemical companies and export buyers | High purity and controlled impurities | Specification-based contract |
| Nickel sulphate | pCAM/CAM and specialty chemical manufacturers | Battery or industrial-grade specification | Long-term or periodic offtake |
| Cobalt sulphate | Cathode and chemical manufacturers | Metal concentration and impurity limits | Specification-based contract |
| Manganese compounds | Battery-material and chemical manufacturers | Product-grade specification | Contract / spot sale |
| Copper and aluminium | Metal processors, smelters and traders | Grade and contamination level | Commodity sale |
| Graphite | Anode-material or industrial users where quality permits | Carbon purity and particle characteristics | Qualification-based |
| EPR certificates | Registered battery producers | Valid CPCB portal generation and category matching | Regulatory compliance transaction |
This distinction is fundamental when preparing the DPR.
A black-mass-only plant has lower processing depth but remains dependent on another refiner. An integrated hydrometallurgical unit can create higher-value outputs but requires more sophisticated technology, utilities, pollution-control systems, laboratory capability and product qualification.
NITI Aayog describes black mass as an intermediate from which hydrometallurgical processing can recover high-purity lithium, cobalt and nickel materials.
Potential buyers can broadly be divided into domestic battery-material manufacturers, cell manufacturers, chemical and metal companies, integrated recyclers and overseas material buyers.
However, investors should be careful with the phrase “battery manufacturer”. A company assembling battery packs may not automatically be a buyer of lithium carbonate, nickel sulphate or mixed black mass. These materials normally need to enter further upstream stages such as cathode active material, precursor or cell manufacturing.
That is why product specification matters as much as recovery percentage.
For example, lithium carbonate produced at insufficient purity may still have a market in ceramics, glass or industrial chemicals, but it may not qualify directly for a battery cathode supply chain.
NITI Aayog specifically identifies this as a current industry constraint. Its January 2026 report states that domestic uptake of recycled battery-grade materials remains limited because India’s battery-component manufacturing ecosystem is still developing, and it identifies the absence of assured long-term offtake and concerns around material quality and consistency as constraints on recycler scale-up.
Therefore, stating that “there will always be buyers for recovered lithium” is not sufficient for a bankable DPR.
A recycler should identify the exact product, specification, buyer category, annual requirement, qualification procedure and commercial formula before finalising the process technology.
An offtake agreement is essentially the commercial bridge between the recycling plant and the downstream customer.
For black mass, pricing can be based on laboratory assay and the contained value of lithium, nickel, cobalt or other recoverable materials. Moisture, fluorine, copper, aluminium and other impurities can affect the payable value.
For refined products such as lithium carbonate, cobalt sulphate or nickel sulphate, the buyer is more likely to qualify the recycler against technical specifications. Material may need laboratory testing, sample approval and consistent production batches before a long-term contract becomes realistic.
For an OEM-linked closed-loop model, the arrangement can be different again. The OEM may send rejected or end-of-life batteries to the recycler and require traceability, recycling documentation and potentially recovered material to be routed back into its supply chain.
Actual industry agreements already illustrate these different structures. Mahindra Last Mile Mobility appointed Attero as a preferred partner for lithium-ion battery disposal and recycling, while VinFast India signed an agreement with BatX Energies in 2025 covering high-voltage battery recycling, material recovery and repurposing.
An example closer to a recovered-material offtake arrangement is LOHUM’s partnership with Glencore, under which LOHUM stated that it would supply 10,000 MT of specialty battery chemicals over five years, including sulphates, carbonates, oxides and cathode-related materials recovered from batteries and other sources.
These examples demonstrate why “offtake” should not be treated as one single market. Feedstock partnerships, recycling-service agreements and recovered-material purchase agreements are commercially different contracts.
The Battery Waste Management Rules, 2022 establish Extended Producer Responsibility obligations for producers placing batteries in the market.
Under the 2023 amendment, EPR certificates for recyclers are linked to waste batteries processed and battery material produced according to CPCB guidelines. The Rules also state that certificates can be used only within the relevant battery category.
This means a compliant recycler can potentially earn revenue from both the physical material recovery chain and the EPR compliance ecosystem.
However, EPR revenue should not be used to justify an otherwise weak recycling project. A sound financial model should separately examine feedstock cost, processing cost, metal recovery, product selling price, EPR income, plant utilisation and commodity-price sensitivity.
As of March 2026, government data showed 520 registered battery-waste recyclers across battery categories, indicating that India’s formal recycling ecosystem is expanding rapidly.
Another major structural driver begins from FY 2027-28.
Under the current binding Battery Waste Management framework, the minimum use of recycled material is set at 5% for portable and EV batteries in FY 2027-28, increasing to 20% from FY 2030-31 onward. Automotive and industrial batteries start at 35% in FY 2027-28 and increase to 40% from FY 2029-30 onward.
This requirement is particularly important for integrated recyclers capable of producing consistent, usable secondary material.
Over time, it should help move the market from a model focused mainly on waste disposal and EPR certificates toward a genuine closed-loop battery-material economy.
The National Critical Mineral Mission has made battery recycling strategically important beyond environmental compliance.
The Government approved a ₹1,500 crore Critical Mineral Recycling Incentive Scheme covering lithium-ion battery scrap, e-waste and other eligible secondary resources. The scheme is designed to support actual extraction of critical minerals rather than facilities that stop only at black mass production.
The government expects the scheme to support at least 270,000 tonnes per annum of recycling capacity, approximately 40,000 tonnes of annual critical-mineral production, around ₹8,000 crore of investment and substantial employment generation. The scheme includes a capital incentive framework subject to its eligibility and implementation conditions.
By April 2026, the Ministry of Mines reported that 58 companies had been found eligible to participate in the scheme.
Budget policy is also attempting to improve feedstock availability. The Union Budget 2025-26 removed Basic Customs Duty on specified lithium-ion battery scrap, while Budget 2026-27 extended customs support to certain capital goods used for critical-mineral processing.
For many investors, the first discussion about a battery recycling plant starts with machinery capacity: 5 TPD, 10 TPD, 20 TPD or 50 TPD.
That is usually too early.
Before finalising capacity, an investor should validate six things: realistic annual feedstock availability by chemistry, signed or highly credible supply channels, expected black-mass yield and metal recovery, downstream product specification, identified buyers with indicative commercial terms, and plant economics under low-utilisation and adverse metal-price scenarios.
This pre-investment work can materially change the technology decision.
A promoter who has reliable black-mass buyers may initially choose mechanical recycling. Another project located near a strong battery-material cluster may justify hydrometallurgical integration. A larger investor may design the plant around imported scrap plus domestic EPR feedstock. Each model creates a different CAPEX, working-capital requirement and risk profile.
The long-term market case is strong, but it should not be described as guaranteed or automatically profitable.
India’s lithium-ion battery demand is expected to expand significantly through EVs and energy storage. End-of-life availability is also projected to rise sharply. EPR creates regulatory demand, recycled-content rules create future material demand, and the National Critical Mineral Mission is supporting deeper domestic recovery.
At the same time, the NITI Aayog data shows a clear near-term challenge: announced recycling capacity can exceed available formal feedstock.
This means the strongest projects are likely to be those that secure both sides of the business before commissioning:
Feedstock → Processing → Recovery → Product Qualification → Buyer → Offtake
Installing machinery without establishing this chain can leave a technically capable plant operating well below design capacity.
A black mass facility is simpler and normally requires less capital than a fully integrated refining facility. Its commercial weakness is that it remains dependent on third-party refiners and black-mass pricing.
Hydrometallurgy allows a recycler to move further downstream into products such as lithium carbonate, nickel sulphate, cobalt sulphate and manganese compounds. These outputs can have higher value, but their commercial success depends on purity, recovery efficiency, operating cost and buyer qualification.
The Government’s critical-mineral recycling incentive structure also clearly signals a policy preference for actual mineral extraction rather than black-mass production alone.
For investors, the correct decision should therefore come from a feasibility study rather than from machinery quotations.
India’s lithium-ion battery recycling sector is entering a high-growth period, but the opportunity is more sophisticated than simply processing future EV waste.
Battery demand could move from approximately 40 GWh in 2025 toward 210 GWh by 2030, while end-of-life battery availability is projected to rise substantially over the following decade. At the same time, India’s currently announced recycling capacity demonstrates that feedstock acquisition, collection networks and downstream offtake will determine which plants actually achieve high utilisation.
For a new recycler, the commercial strategy should therefore be prepared alongside the technical DPR.
A strong project should answer three questions before major CAPEX is committed:
Where will the batteries come from? What exactly will the plant produce? Who has agreed to buy that output?
Green Permits can support investors planning lithium-ion battery recycling projects with market and feasibility assessment, DPR preparation, capacity planning, technology and process evaluation, plant layout, pollution-control planning, CTE/CTO roadmap, Battery Waste Management compliance and CPCB/SPCB registration strategy.
