What a Varanasi Data Center Actually Has to Treat
A data center in Varanasi needs to treat four distinct water streams: cooling tower makeup (drawn from municipal supply or the Ganga), cooling tower blowdown (a brackish, silica-rich concentrate with TDS typically 1,200–6,000 mg/L), low-volume process wastewater from humidification and chiller plant drains, and sanitary sewage. Because 70–80% of evaporative cooling water is consumed and only 20–30% leaves as blowdown (KETOS, 2026), the priority is a side-stream filtration plus RO train sized for 60–85% blowdown recovery, followed by a discharge polishing step that meets CPCB effluent norms applicable to inland surface water discharge. Treatment selection should be driven by the local source water chemistry, cooling tower cycles of concentration, and the operator's reuse-versus-discharge strategy, not by generic U.S. cost benchmarks.
Cooling towers dominate the water balance for most Indian hyperscale and colocation campuses. Industry estimates put water-based cooling as the primary method at 75–90% of data centers worldwide (KETOS, 2026), and in evaporative systems roughly 70–80% of water withdrawn is consumed by evaporation with the remaining 20–30% discharged as blowdown (KETOS, 2026). The volumetric anchor for Varanasi sizing: a 100 MW facility can require up to about 2 million liters of water per day (IDE Tech, 2026). At that scale, blowdown generation is the second-largest stream after evaporation and the one that drives discharge compliance work.
The four streams fall into two operational groups. Cooling-related streams — makeup and blowdown — are high-volume, continuous, and dominated by inorganic scaling species (calcium, magnesium, silica, alkalinity) plus treatment chemicals such as biocides and corrosion inhibitors. Low-volume process wastewater and sanitary sewage are intermittent, lower in dissolved load, and typically handled by a packaged STP that does not interact with the cooling water chemistry. A Varanasi project engineer should size the cooling-side treatment train against the local source water profile, not against a generic benchmark: the Ganga and most municipal supplies in eastern UP carry monsoon-driven turbidity swings, and the Indo-Gangetic plain pushes makeup TDS higher than the global averages seen in published U.S. case studies (KETOS, 2026). Request a seasonal lab panel — pre-monsoon, monsoon, post-monsoon — before fixing the design, because the blowdown envelope you size the RO around is set by the worst-case makeup mineral load, not the annual average.
Cooling Tower Blowdown: The Stream Worth Designing Around
Cooling tower blowdown is a controlled purge to keep cycles of concentration inside the scaling and corrosion envelope of the cooling water chemistry program. At 4 cycles of concentration, about 25–30% of makeup water is lost as blowdown, so a 10 million gallon/month facility discharges 2.5–3 million gallons monthly (Genesis Water Technologies, 2026). Push the cycles higher and the blowdown volume drops, but the per-liter contaminant load climbs — which is why the same project that saves freshwater by raising cycles also creates a more aggressive treatment train downstream.
For a Varanasi project, the blowdown quality parameters below should be requested from the cooling water chemistry vendor and verified against a lab panel on the actual makeup water. They are the inputs that fix RO recovery, antiscalant dose, and discharge polishing requirements.
| Parameter | Typical blowdown range | Design implication for Varanasi |
|---|---|---|
| TDS | 1,200–6,000 mg/L (4–8× makeup) | Sets RO feed osmotic pressure and recovery ceiling; Indo-Gangetic mineral content pushes the upper end |
| Suspended solids | 10–50 mg/L even with basin filtration | Drives the sidestream filter and UF sizing ahead of any RO |
| Scaling species | Ca, Mg, silica, alkalinity concentrated alongside treatment chemicals | Limits BWRO recovery to 75–80% before silica and CaSO4 scaling dominate (IDE Tech, 2026) |
| Treatment chemicals | Biocides, corrosion/scale inhibitors, dispersants; legacy chromate or high-phosphate programs are problematic | Antiscalant selection and biocide neutralization must be matched to the existing cooling program |
| Biological load | Planktonic bacteria, algae, biofilm fragments | Needs to be addressed before any membrane step |
| Discharge cost reference | $5–15 per thousand gallons in water-stressed regions; some jurisdictions cap TDS below 1,500 mg/L (Genesis Water Technologies, 2026) | Direct discharge into the Ganga basin is constrained by CPCB norms, so reuse economics usually beat disposal economics |
Two points from this table drive most of the Varanasi design. First, the scaling ceiling is a chemistry problem, not an equipment problem: a conventional BWRO that pushes past 75–80% recovery on blowdown will foul on silica and calcium sulfate unless the architecture is changed (IDE Tech, 2026). Second, the discharge envelope in the Ganga basin is governed by CPCB effluent norms applicable to inland surface water, not by a U.S. tipping fee, so the reuse case has to be made on avoided freshwater intake and reduced discharge volume rather than on avoided disposal cost.
Matching the Treatment Train to Varanasi Source Water

Build the train from the upstream end down. Start with side-stream or self-cleaning mechanical filtration on the cooling loop: spiral units delivering 10–25 micron filtration, sized at 1–5% of circulation flow, with CAPEX in the $50,000–200,000 range for typical data center installations (Genesis Water Technologies, 2026). This step is what keeps the downstream membranes clean and is the cheapest kilogram of suspended solids you will ever remove.
Next, add ultrafiltration pretreatment for blowdown RO ahead of the RO. UF with 0.01–0.1 micron PVDF hollow-fiber membranes, low-pressure operation at 10–30 psi, 90–95% recovery, and periodic backwash with chemical cleaning every 1–3 months (Genesis Water Technologies, 2026) takes out the biological load and colloidal solids that pass a media filter. The industrial RO system for cooling blowdown then does the bulk dissolved-solids cut: permeate typically reaches 10–50 mg/L TDS, removes 95–99% of hardness, silica and treatment chemicals, runs at 150–400 psi, and recovers 50–85% of the blowdown feed (Genesis Water Technologies, 2026).
Respect the 75–80% recovery ceiling on a conventional BWRO. Pushing past it on a Varanasi makeup — where silica, calcium, and sulfate are all present at Indo-Gangetic levels — requires a different design philosophy, not just a larger pump. The high-recovery architectures described in the research (IDE Tech, 2026) manage the scaling problem at the system level: RO runs at a conservative local recovery, and the concentrate is routed to a step that precipitates silica, calcium carbonate, and other problematic salts onto seed material as compact pellets that are withdrawn as a solid waste stream. The remaining brine is dominated by sodium chloride and can be processed further. This translates into a concrete process step that an Indian EPC team can map against a P&ID: RO permeate to cooling makeup, RO concentrate to controlled salt precipitation, precipitated solids to solid waste handling, residual brine onward to disposal or further concentration.
Use nanofiltration when the discharge or reuse limit is driven by hardness rather than total TDS. NF operates at 75–150 psi, achieves 70–85% recovery, and lets monovalent ions pass (Genesis Water Technologies, 2026), which is useful if the operator wants to blend NF permeate with raw makeup to raise cycles of concentration without committing to a full RO energy budget. Close the train with discharge polishing sized against the parameters a Varanasi facility is most likely to be measured on — residual chlorine/biocide, TDS, and any state-specific effluent parameters — rather than copying a U.S. ZLD layout that the research flags as a $3–8M CAPEX option justified only in severely water-scarce, no-discharge contexts (Genesis Water Technologies, 2026).
Reuse, Discharge or ZLD: The 2026 Decision Framework
Pick the end-of-pipe strategy before you finish equipment sizing. The three options — cooling tower makeup reuse, discharge compliance, and zero liquid discharge — have very different unit operations, capital profiles, and regulatory framings, and they are not interchangeable on a Varanasi project where the Ganga basin discharge envelope is fixed.
| Strategy | Treatment path | Recovery | Typical CAPEX | OPEX | When it fits Varanasi |
|---|---|---|---|---|---|
| Cooling tower makeup reuse | Sidestream filter + UF + RO, permeate blended back into cooling loop | 60–85% (Genesis Water Technologies, 2026) | Aligned to the RO benchmark below | $1.50–3.00 per 1,000 gal treated (Genesis Water Technologies, 2026) | Default path — cuts freshwater intake and discharge volume simultaneously |
| Discharge compliance | TDS reduction, metals removal, biocide neutralization sized to CPCB effluent norms | Not the goal; goal is permit compliance | Lower than reuse train | Avoided discharge fees; savings depend on local tariff | Use when reuse is not feasible and the priority is meeting permit limits on TDS, metals, or biocide residuals |
| Full ZLD | RO/NF (70–80%) → MVC or brine concentrator (95%) → crystallizer | 95–99% (Genesis Water Technologies, 2026) | $3–8M (Genesis Water Technologies, 2026) | $5–15 per 1,000 gal (Genesis Water Technologies, 2026) | Only where discharge is prohibited or freshwater is unavailable |
| Partial ZLD | MVC or brine concentrator on RO concentrate, no crystallizer | Reduces liquid volume by 80–90% | $1–3M for 10,000–30,000 GPD MVC (Genesis Water Technologies, 2026) | 15–25 kWh per 1,000 US gallons of distillate (Genesis Water Technologies, 2026) | Practical middle path for a Varanasi facility that wants to limit discharge without a crystallizer |
The decision rule is straightforward. Cooling tower makeup reuse is the strongest value path because it cuts freshwater intake and discharge volume at the same time, and the permeate feeds directly back into a use point the operator already controls (Genesis Water Technologies, 2026). Discharge compliance is the right choice when reuse is not feasible and the permit is the binding constraint. ZLD is a $3–8M CAPEX commitment (Genesis Water Technologies, 2026) that has to be justified against a real no-discharge scenario, not against generic water-stewardship language. Partial ZLD — concentrating blowdown to reduce liquid volume by 80–90% — captures most of the volume benefit at substantially lower cost and is the path a Varanasi project should evaluate before sizing a full crystallizer.
Match the strategy to the regulatory context. Discharge into the Ganga or its tributaries falls under the CPCB framework applicable to inland surface water, and reuse as cooling makeup must stay compatible with the existing cooling water treatment program. The research is explicit that legacy chrome- and phosphate-heavy chemistries create reuse and discharge problems simultaneously (Genesis Water Technologies, 2026), so any vendor proposing a high-recovery train on top of a legacy chemistry program should be asked to show how they will handle that interaction. Chlorine dioxide generation for biocide control and antiscalant and biocide dosing for the blowdown train are two unit operations the EPC team should see named explicitly in the P&ID before signing off on the bid.
Cost, Footprint and Sizing Anchors for a 2026 Varanasi Campus

Use the ranges below as order-of-magnitude anchors when you brief procurement. They are U.S.-sourced benchmarks (S2, S4) and will not match Indian EPC numbers exactly, but they give you a defensible starting band and a way to challenge vendor numbers that look too good to be true.
RO train benchmark: a 50,000 GPD blowdown RO system installed costs roughly $250,000–500,000 with OPEX of $1.50–3.00 per thousand gallons treated, covering energy, chemicals, membrane replacement and maintenance (Genesis Water Technologies, 2026). Side-stream filtration benchmark: $50,000–200,000 CAPEX for typical data center installations, with operating costs dominated by occasional solids disposal and routine maintenance (Genesis Water Technologies, 2026). Evaporative concentration benchmark: MVC systems at 95–98% recovery cost $1–3M for 10,000–30,000 GPD capacity and consume 15–25 kWh per 1,000 US gallons of distillate, making them the typical second stage of a partial- or full-ZLD train (Genesis Water Technologies, 2026). ZLD total: $3–8M CAPEX and $5–15 per thousand gallons OPEX, with solid waste below 1% of original blowdown volume — a useful upper-bound reference even for a reuse-focused project (Genesis Water Technologies, 2026). For the membrane design itself, the RO membrane design criteria guide walks through feedwater characterization, flux, and array staging in the same engineering language your vendor will use.
A sizing check a Varanasi engineer should run before committing to a number: take the 100 MW, ~2 million liters/day anchor (IDE Tech, 2026) and apply the 70–80% evaporation / 20–30% blowdown split (KETOS, 2026). At 4 cycles, blowdown is 25–30% of makeup (Genesis Water Technologies, 2026), so a 2 MLD site pushes 500,000–600,000 L/day to the treatment train. That is the flow your RO sizing has to handle, and the same number your discharge permit envelope has to accommodate. Anything significantly off that band should be questioned — either the cooling water chemistry program is being run at much higher cycles than published, or the evaporation ratio assumption is wrong.
Two cautions. The cost figures above are order-of-magnitude anchors only; 2026 Indian project costs will reflect different equipment sourcing, EPC labor rates, and CPCB-driven monitoring scope. And the blowdown quality numbers — TDS 1,200–6,000 mg/L, suspended solids 10–50 mg/L (Genesis Water Technologies, 2026) — are framework ranges, not a Varanasi-specific lab result. The seasonal source-water panel you commission on the Ganga or the municipal intake will set the actual feed numbers your RO has to handle.
Frequently Asked Questions
What blowdown treatment train should a hyperscale data center in Varanasi actually specify?
Specify a side-stream or self-cleaning mechanical filter (10–25 micron) sized at 1–5% of circulation flow, followed by UF pretreatment (0.01–0.1 micron PVDF, 10–30 psi, 90–95% recovery) and an RO unit running 50–85% recovery on blowdown to deliver 10–50 mg/L TDS permeate (Genesis Water Technologies, 2026). Hold the conventional BWRO recovery at or below 75–80% to stay ahead of silica and calcium sulfate scaling on Indo-Gangetic source water (IDE Tech, 2026), and ask the vendor to name the unit operation that handles residual concentrate — precipitation loop, MVC, or direct discharge polishing — rather than leaving it as a line item.
How much should a 2026 data center budget for blowdown RO and pretreatment in India?
Treat published CAPEX as order-of-magnitude only. A 50,000 GPD blowdown RO system installs at roughly $250,000–500,000 with OPEX of $1.50–3.00 per thousand gallons treated, and side-stream filtration adds $50,000–200,000 on top (Genesis Water Technologies, 2026). Request an India-specific quote that breaks out membrane area, high-pressure pump rating, antiscalant program, and CPCB monitoring scope; the U.S. anchor is the starting point for negotiation, not the answer. For a full ZLD scope, plan against $3–8M CAPEX and $5–15 per thousand gallons OPEX (Genesis Water Technologies, 2026), and only if discharge is genuinely prohibited.
What should a Varanasi project verify locally before signing a vendor order?
Commission a seasonal source-water panel covering pre-monsoon, monsoon, and post-monsoon conditions on the actual intake (Ganga or municipal supply) and ask the vendor to run their RO projection against the worst-case mineral load, not the annual average. Confirm the existing cooling water treatment program — legacy chromate or high-phosphate chemistries will create reuse and discharge problems simultaneously (Genesis Water Technologies, 2026) and may need to be reformulated before the blowdown train can run at the recovery the vendor is quoting. And ask for a CPCB effluent-norm compliance check on the proposed discharge path, because the Ganga basin envelope is the regulatory ceiling that fixes the polishing step, not a U.S. discharge fee.
How do I choose between a hyperscale-grade supplier and a local Indian EPC for the blowdown train?
Match the supplier to the highest-risk unit operation in the train. For the RO itself, prefer a vendor with documented high-recovery blowdown experience — the MAXH₂O-style architecture described in the research (IDE Tech, 2026) is a real engineering choice, not a sales line, and the supplier should be able to explain how they handle silica and calcium sulfate precipitation at the recovery they are quoting. For civil work, tanks, and the automatic chemical dosing system integration, a local EPC with prior data center work typically delivers better schedule and cost outcomes. Ask both sides to nominate a single point of accountability for the integrated train, and verify that the EPC's P&ID names the same unit operations the RO vendor is specifying.
Related Equipment
- industrial RO system for cooling blowdown — specifications, capacity range, and technical data
- multi-media filter for makeup water — specifications, capacity range, and technical data