A promoter had almost finalised an industrial plot for a recycling project.
The land was affordable, the highway was less than 10 km away, labour was available nearby, and the owner had assured him that electricity and water would not be a problem. On paper, it looked like the right location.
Then the engineering team began working on the actual plant.

The proposed facility was not just a dismantling unit. It would receive lithium-ion battery waste, carry out mechanical preprocessing, generate black mass and later add a chemical recovery line for extracting valuable materials. That changed the project completely.
The electrical load was higher than expected. The plot needed separate areas for incoming batteries, damaged material, black mass, chemicals and residues. Space was required for an effluent treatment plant, fire movement, pollution-control equipment and future expansion. Tanker water alone was no longer considered a comfortable long-term solution.
The cheapest plot was suddenly not the cheapest project.
This is one of the most important lessons in critical mineral recycling site selection. Land should not be selected first and the process fitted into it later. The project should move in the opposite direction.
First define the feedstock, recycling technology, capacity, products and utilities. Then identify the land that can support them.
For promoters planning battery recycling, e-waste processing, black mass refining or other critical mineral recovery facilities in India, location selection can affect CAPEX, operating cost, approvals, feedstock security and ultimately the commercial viability of the plant.
Critical mineral recycling is receiving increasing attention in India because industries such as electric vehicles, electronics, renewable energy and energy storage depend heavily on materials such as lithium, cobalt, nickel, copper and other strategic minerals.
India has also introduced a ₹1,500 crore Critical Mineral Recycling Incentive Scheme to encourage recovery of critical minerals from secondary sources.
By 30 April 2026, 58 companies had reportedly been found eligible under the scheme. These companies together represented approximately 850 KTPA of pledged recycling capacity and around ₹5,000 crore of proposed investment.
These figures represent pledged projects and should not be confused with fully commissioned operating capacity. However, they indicate the scale at which critical mineral recycling projects are beginning to move forward.
For new investors, this means the discussion is changing.
The question is no longer only:
“Is there an opportunity in critical mineral recycling?”
It is increasingly:
“Where should the plant be located, what infrastructure will it need, and can the proposed site support the complete recovery process?”
That is where proper site selection becomes important.
There is no standard critical mineral recycling factory.
Two companies may both describe their projects as lithium-ion battery recycling plants while operating completely different processes.
One company may receive battery packs, discharge them, dismantle modules, shred cells and generate black mass.
Another company may purchase black mass directly and operate a hydrometallurgical facility for recovering lithium, cobalt, nickel or manganese compounds.
A third company may establish an integrated facility covering collection, dismantling, mechanical separation, black mass generation and chemical recovery.
Each project has a different land requirement, utility load and environmental footprint.
A good project sequence is therefore:
Feedstock -> Capacity -> Technology -> Machinery -> Material Balance -> Utilities -> Pollution Control -> Plant Layout -> Site Selection
Many projects make the mistake of reversing this sequence.
They first acquire industrial land and then try to determine what capacity and process can fit inside it. That approach can create expensive compromises later.
Before evaluating any location, management should clearly define:
Only after these are reasonably clear should the land search become serious.
Feedstock affects almost every location decision.
A battery recycler may handle:
An e-waste-based critical mineral recovery project may instead receive printed circuit boards, electronic assemblies, components or selected high-value fractions.
These materials have different storage, handling, fire, transport and processing requirements.
For example, a plant receiving complete EV batteries needs space for safe unloading, inspection and segregation. A plant buying black mass directly may require considerably less space for dismantling but substantially more chemical-processing infrastructure.
This is why a 10 TPD preprocessing unit and a 10 TPD hydrometallurgical recovery plant cannot automatically be planned on the same assumptions simply because the throughput number is identical.
One of the most common questions from investors is:
“How many acres are required for a critical mineral recycling plant?”
There is no single statutory acreage that can be applied to every project.
The correct land area depends on what will actually happen inside the facility.
Instead of beginning with acreage, divide the proposed project into functional zones.
A typical integrated facility may require space for:
The actual usable area of a plot can matter more than the total acreage.
A rectangular 2-acre industrial plot with proper road frontage and logical movement may sometimes be more useful than a 3-acre irregular site where production, storage and truck circulation cannot be arranged efficiently.
Land planning should therefore be linked directly with the preliminary plant layout.
A low-cost property is useful only if the proposed industrial activity can legally and practically operate there.
Before purchasing or entering into a long-term lease, the promoter should verify the land-use position and the industrial activity permitted at the location.
This becomes especially important when the project involves chemical recovery, metallurgical processing or hazardous-material handling.
Do not rely only on statements such as:
“It is industrial land.”
A recycling project should be evaluated against the actual proposed activity.
Questions should include:
These checks should ideally happen before major land payments are made.
Power availability is one of the most underestimated elements of recycling site selection.
A property owner may say that electricity is available, but that does not necessarily mean the required electrical load can be sanctioned quickly or economically.
Critical mineral recycling equipment may include:
If the project later moves into metallurgical recovery, electrical and thermal requirements can increase further.
Before finalising the site, prepare at least a preliminary connected-load schedule.
For example, an investor may initially estimate that a 500 kVA connection will be sufficient. Once the mechanical line, pollution-control system, pumps, utilities and expansion provision are included, the actual requirement may move closer to 1,000 or 1,250 kVA.
Those numbers are only an illustrative example, but they show why utility planning must happen before land commitment.
Management should confirm:
The cost difference between two sites can change significantly once electrical infrastructure is included.
A dismantling or mechanical preprocessing unit may use relatively little process water.
A hydrometallurgical recovery plant is different.
Water may be required for:
For this reason, every serious site-selection study should include a preliminary water balance.
The project team should calculate:
Fresh water requirement -> Process consumption -> Recovered water -> Wastewater generation -> Treatment -> Reuse -> Final permissible discharge or disposal
Suppose an illustrative project calculates an average fresh-water requirement of 20 KLD during its first phase. If Phase 2 chemical recovery increases the requirement to 45 KLD, a site dependent entirely on uncertain tanker supply may become commercially weak.
Again, these figures are examples rather than standard requirements.
The important point is that the water source should be matched with the full project, including planned expansion.
One of the most frequent layout mistakes in industrial projects is designing the production line first and asking later:
“Where will the ETP go?”
Environmental infrastructure should be planned from the beginning.
Depending on the recovery process, the facility may require:
These systems require real land.
They also require maintenance access, piping, safe movement and operational separation from production areas.
A recycling plant should therefore be planned as one integrated industrial system, not as a production line with environmental equipment added around it later.
Environmental approvals should reflect the actual project configuration.
For e-waste recyclers, the CPCB framework links recycler capacity with the capacity reflected in the Consent to Operate. The application also requires details relating to the recycling facility, process, installed machinery and recovered products.
Battery recyclers similarly operate within the Battery Waste Management framework and require appropriate registration through the applicable authority and portal mechanism.
The project documentation should therefore remain consistent.
The following should ideally describe the same plant:
DPR -> Process Flow -> Plant Layout -> CTE -> Machinery Installation -> Pollution Controls -> CTO -> Recycler Registration
Problems can arise where one document shows 5,000 TPA, another shows 10,000 TPA and machinery quotations suggest an entirely different capacity.
Capacity planning should therefore happen early.
A recycling plant without reliable feedstock is simply an expensive industrial building.
Critical mineral projects should map feedstock before choosing the location.
Potential sources can include:
Distance alone is not enough.
The promoter should estimate the delivered cost of feedstock.
A simple framework is:
Delivered Feedstock Cost = Material Purchase Cost + Collection + Handling + Packaging + Transportation + Sorting Loss + Compliance Cost
Suppose one state offers industrial land that is ₹30 lakh cheaper than another location.
That saving may look attractive.
But if the plant processes 10,000 tonnes annually and the cheaper location adds even ₹800 per tonne in average inbound logistics, the additional annual transport burden can reach approximately ₹80 lakh.
That single calculation can reverse the site decision.
This is why land price should never be studied independently from feedstock geography.
Most site-selection studies focus heavily on waste availability but give less attention to the finished material.
That is a mistake.
A critical mineral recycler may sell black mass, recovered metals, salts, compounds or other intermediate materials.
The project should understand where those buyers are located.
Similarly, a hydrometallurgical operation may require regular supplies of acids, alkalis, reagents, packaging materials, laboratory consumables and specialised equipment.
The more sophisticated the recovery process becomes, the more important industrial ecosystem access can become.
A useful location-cost framework is:
Total Location Cost = Land + Power Infrastructure + Water + Inbound Logistics + Chemicals + Waste Handling + Outbound Logistics + Labour + Compliance Infrastructure
This is much more meaningful than comparing land rent alone.
Critical mineral recovery does not convert every kilogram of incoming waste into a saleable product.
Residues will remain.
Depending on the technology, these may include:
Their classification and disposal route depend on the actual process.
Before selecting a site, promoters should understand where these materials will go and what downstream authorised facilities are available.
If every tonne of residue has to travel several hundred kilometres, disposal costs can become a meaningful operating expense.
Consider an illustrative company planning a 10,000 TPA lithium-ion battery recycling project.
The first phase will include dismantling, shredding and black mass production. The promoter also wants enough land and infrastructure to add hydrometallurgical recovery after approximately 2 years.
Two sites have been shortlisted.
Site A is cheaper and located close to the battery-waste catchment.
Land cost is attractive, and inbound transportation is expected to be lower.
However, preliminary review identifies several concerns.
The existing electrical infrastructure may not comfortably support the Phase 2 load. Water availability requires further confirmation. The plot is also tight once production, storage, fire movement, ETP and the future chemical-recovery block are included.
Site B costs more.
However, it is located inside a stronger industrial ecosystem. Larger electrical connections are available nearby, chemical suppliers operate within the region and authorised waste-treatment infrastructure is easier to access.
Buyer connectivity is also better.
If management compares only land price, Site A appears stronger.
But after calculating electrical upgrades, additional residue transportation, Phase 2 civil modification and expansion constraints, the financial difference becomes much smaller.
The case study demonstrates an important principle:
The best recycling location is not the plot with the lowest land cost. It is the site with the lowest long-term cost of operating the complete project.
A simple way to shortlist critical mineral recycling locations is to evaluate them through three separate gates.
First determine whether the project has a workable approval pathway.
Review:
If the site fails this gate, there is little value in analysing cheap land or logistics.
Next determine whether the plant can physically operate there.
Review:
Finally compare the full commercial impact.
Review:
A site should ideally clear all three gates before a major investment decision is made.
Before purchasing or leasing land for a critical mineral recycling project, management should be able to answer these 12 questions clearly:
If several of these questions are still unanswered, the project is probably not ready for final land commitment.
Critical mineral recycling site selection should not begin with a property broker.
It should begin with the process.
Define the feedstock, capacity, technology, material balance and products first. Then calculate the machinery, power, water, environmental systems, storage and logistics required to support them.
After that, compare locations.
For a mechanical preprocessing project, feedstock access, storage, power and fire safety may dominate the decision.
For an integrated hydrometallurgical or metallurgical project, water availability, chemical infrastructure, pollution control, hazardous-waste management and regulatory suitability become much more important.
The right site is therefore not necessarily the cheapest industrial plot.
It is the location where the complete project can be approved, constructed, supplied, operated and expanded without repeatedly redesigning the business around limitations that should have been identified before the land was selected.
Green Permits supports investors and recyclers with critical mineral project feasibility, site evaluation, DPR preparation, plant layout and utility planning, CTE/CTO support, recycling approvals and complete plant implementation advisory.
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