Semiconductor fabrication plants (fabs) manage water as a process material, a cooling and utility resource, and a pollution-control input. They take in water from local or utility supplies, purify part of it to ultrapure-water (UPW) quality, keep wastewater streams separate when their contaminants require different treatment, reuse water where its quality and the application allow, and discharge the remainder under permits. The exact treatment train, recycling rate, water source and environmental risk vary by facility and watershed.
Water is only one part of a fab’s environmental profile. Energy-intensive purification, treatment chemicals and residuals, local basin stress, permitted discharges, and fluorinated greenhouse-gas emissions from wafer processing all need to be considered together.
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Why semiconductor fabs need so much water
Wafer manufacturing uses water repeatedly for rinsing, wet etching, solvent processing and planarization. Those steps require UPW, whose ionic, organic and particle content is controlled far more tightly than ordinary industrial or municipal water. A fab also uses water outside the wafer process: cooling systems, facility utilities and pollution-control equipment such as exhaust scrubbers all require reliable supplies.
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Water uses reported in an industry assessment
A NIST programmatic environmental assessment published in June 2024, citing an IEEE 2023 study, attributed the following shares of facility water use to the study’s semiconductor sites:
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| Use category | Share reported in the cited study | Examples |
|---|---|---|
| Semiconductor processing | 48% | Wafer production, wet etching, solvent processing and planarization |
| Facility support | 23% | Cooling and related plant utilities |
| Abatement technologies | 20% | Equipment that controls process exhaust and other pollutants |
These percentages describe the cited study, not a standard allocation for every fab. A plant’s product mix, climate, cooling design, abatement equipment and water-recovery projects can change the balance.
UPW requires more incoming water than the final product volume
UPW is made through multiple physical and chemical treatment steps. Reject water and losses in pretreatment, membrane systems and polishing mean that the incoming volume can exceed the amount delivered as UPW. The NIST assessment, citing Govindan (2022), reports that producing 1,000 gallons of UPW can require approximately 1,400 to 1,600 gallons of municipal water. The ratio is an estimate represented in that assessment, not a guarantee for every plant or treatment design.
The same NIST assessment, citing Wang and colleagues, reports median UPW use of 4.25 billion gallons across 29 facilities in 2021, equivalent to 1.16 million gallons per day. That figure describes the 29-facility dataset and should not be read as the daily demand of a typical individual fab.
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1. Source water enters a controlled plant system
Fabs obtain water through local utilities, municipal systems or other permitted sources. Engineers must examine both the reliability of that supply and the watershed from which it is drawn. A large, dependable connection does not eliminate drought, allocation or community-supply risks if the surrounding basin is already stressed.
2. Pretreatment protects the UPW equipment
Incoming water is conditioned before it reaches the final UPW polishing stages. Pretreatment removes suspended material and reduces constituents that would foul membranes, ion-exchange equipment or other purification units. The required sequence depends on source-water chemistry and the UPW specification for the process tools.
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3. UPW is distributed to process tools
Once purified, UPW is circulated to wafer-production tools and rinsing points. The system must maintain the required quality at the point of use, not merely at the treatment plant outlet. Process areas may use UPW for wet etching, solvent processing, planarization and repeated rinses.
4. Separate utility and abatement loops operate alongside process water
Cooling equipment, scrubbers and other facility systems may accept water with a different quality requirement from UPW. Keeping these applications distinct can prevent over-treating water that does not need semiconductor-grade purity and can make recovery projects more practical.
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Water leaving a fab can come from etching and post-process rinses, cleaning and degreasing, polishing, UPW-reject systems, cooling operations, scrubbers and other support activities. Each stream can carry a different combination of dissolved chemicals, particles, metals, fluorides, organics or changes in pH. Combining all flows at the first drain can make treatment less efficient and can expose a low-contaminant stream to contaminants that would otherwise have been easier to recover.
Representative streams and management needs
| Source activity | Why it is separated or characterized | Examples of treatment or handling reported by EPA |
|---|---|---|
| Etching and post-process rinsing | Can carry process chemicals and constituents that require chemistry-specific control | pH adjustment, clarification, chemical precipitation, filtration and fluoride treatment |
| Cleaning and degreasing | May contain cleaning chemicals and organic compounds | Segregated collection and treatment selected for the contaminants present |
| Polishing, cutting and grinding | Can add particles and process residues to the water | Clarification and filtration, with additional treatment where required |
| UPW reject and rinse water | Often has lower contaminant concentrations than concentrated process waste, but its quality still determines whether recovery is practical | Reuse in later rinses, cooling towers or scrubbers in facility examples documented by EPA |
EPA’s 2022 study identifies fluoride, arsenic and organic compounds among pollutants associated with electrical and electronic component wastewater. The list is not a claim that every fab discharges each pollutant; actual constituents depend on chemicals, materials, equipment and operating conditions.
How treatment, reuse and discharge fit together
Step 1: Characterize each stream
Operators measure flow, pH, conductivity and the contaminants relevant to the process. Sampling and monitoring establish whether two streams can share a treatment stage or whether they need separate tanks, controls and permits.
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Step 2: Segregate compatible and incompatible flows
High-strength or chemistry-specific streams are kept apart from cleaner rinse water when that improves treatment, recovery or compliance. Stream segregation is a central design principle in SEMI F98 guidance because the reuse option depends on water quality and the intended application.
Step 3: Apply a treatment train matched to the contaminants
Facility examples reported to EPA include pH adjustment, clarification, chemical precipitation, filtration, fluoride treatment and specialized processes for particular contaminants. No single sequence applies to every fab. Treatment selection must account for incoming chemistry, target discharge limits, residuals, reliability and the quality needed for the next use.
Step 4: Send recovered water to an application that can accept its quality
SEMI F98 describes potential destinations for appropriately treated water: the front end of the UPW system, cooling systems, exhaust scrubbers, point-of-use abatement, thermal processes and site irrigation. EPA’s facility examples also include using rinse water in subsequent rinses, cooling towers or scrubbers. Reuse is therefore a matching exercise: the water must meet the receiving system’s quality and operational requirements, and the arrangement must comply with environmental rules.
Step 5: Treat and manage residuals
Purification and wastewater treatment do not make contaminants disappear. Concentrates, filter media, precipitated solids and other residuals require controlled handling and disposal or further processing. A project that lowers freshwater withdrawal but creates difficult residuals still needs a complete environmental evaluation.
Step 6: Discharge the remaining water under the applicable authorization
Reuse reduces the volume requiring discharge; it does not automatically produce zero liquid discharge. EPA’s 2022 study reported that industry contacts did not know of U.S. semiconductor facilities operating as zero-discharge plants at the time of that study.
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How much water do fabs recycle?
Recycling claims must identify the denominator, the date and the type of water being measured. The NIST assessment reports two different measures:
| Measure | Reported result | Qualification |
|---|---|---|
| Recycling of received water | 40% to 70% average as of 2022 | Reported for fabs using conventional onsite treatment; cited by NIST from IEEE (2023) |
| UPW recycling for process activities | More than 80% at several large manufacturers | Company or facility reports cited by NIST from Wang et al. (2023a, 2023b); this is not the same denominator as received-water recycling |
An UPW-process recycling rate above 80 percent can coexist with a lower percentage for all water received by the site because cooling, abatement, sanitation and other uses may follow different loops. Neither figure should be generalized to every fab.
Independent reader supportYour contribution helps us test, update, and keep practical guides available for everyone.Discharge permits and U.S. regulatory requirements
EPA’s electrical and electronic components rules
In the United States, EPA’s Electrical and Electronic Components (E&EC) effluent guidelines apply to direct dischargers that release wastewater to U.S. waters and to indirect dischargers that send it to publicly owned treatment works. The requirements are incorporated into permits or other control mechanisms. The rule framework covers wastewater associated with activities such as etching, cleaning, degreasing, cutting and grinding.
What the current EPA review says
EPA’s E&EC effluent-guideline page, updated March 17, 2026, says the agency’s detailed study found no demonstrated need to revise the existing regulation at that time. EPA also says the PFAS data it reviewed were limited and that it intends to continue monitoring discharges. That statement describes EPA’s review posture; it does not establish that every facility is free of PFAS or that other federal, state, local or pretreatment requirements are irrelevant.
Why a permit review is site-specific
A project team must determine whether a fab discharges directly, sends wastewater to a public treatment works, or uses a combination of routes. The receiving water or treatment works, local limits, monitoring obligations, pretreatment approval and chemical inventory can all affect the final permit conditions. U.S. requirements should not be presented as a worldwide standard: other jurisdictions impose their own rules.
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Water risk depends on the watershed
The same withdrawal volume can have very different consequences in two locations. A basin with abundant seasonal flows and strong municipal infrastructure presents a different risk profile from a drought-prone basin where residents, farms and ecosystems already compete for limited supplies. The source and destination of water matter as much as the volume reused onsite.
SEMI’s October 2025 global assessment description says it analyzed 140 semiconductor production facilities across 89 water basins to establish a baseline of water-risk hotspots. The number of basins demonstrates why basin-level analysis is important; it does not mean that all 140 facilities face the same degree of risk.
NIST’s 2024 assessment, citing Wang et al. (2023a), reports that global semiconductor-industry water use increased 24.5 percent from 2019 to 2023. Industry growth can increase pressure on supplies unless fabs, utilities and regulators achieve additional reductions in withdrawals, consumption and discharges.
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Energy and chemical trade-offs
UPW production is energy- and cost-intensive because it uses multiple physical and chemical treatment steps. Higher reuse can reduce freshwater withdrawals, but recovery equipment also consumes energy, chemicals and maintenance resources and may produce concentrates or solids. The net benefit depends on the treatment route, source-water quality, reuse application and local electricity and waste-management conditions.
Fluorinated greenhouse-gas emissions
Water treatment does not control every important fab emission. EPA explains that fluorinated gases are used in plasma etching and in cleaning chemical-vapor-deposition chambers. EPA identifies process optimization, alternative input gases and destruction technologies as mitigation approaches and tracks facility-specific emissions through Greenhouse Gas Reporting Program Subpart I. These air-emission controls should be evaluated alongside, not substituted for, wastewater management.
Community and receiving-system effects
Discharge quality, temperature, flow timing and residual contaminants can affect a receiving stream or a public treatment works. A compliant discharge can still warrant watershed-level attention when several industrial users draw from or discharge to the same system. Community engagement and transparent reporting help identify supply, drought and infrastructure concerns that a plant-boundary recycling percentage cannot show.
How to compare two fabs or two reuse projects
Use the following questions before treating one recycling claim as better than another:
Quick Recap
- What is the water source and basin condition? Identify the utility or source arrangement, local water stress and competing users.
- What does the reported percentage measure? Distinguish withdrawal, consumption, internal recycling, UPW recycling and reclaimed-water supply.
- Which streams are segregated? Check whether concentrated process wastewater, cleaner rinses, UPW reject, cooling water and scrubber flows are managed separately.
- What treatment train is used? Look for the contaminant-specific stages, monitoring points, residual management and backup capacity.
- Where does recovered water go? Confirm the quality requirement for UPW feed, cooling, scrubbers, abatement, thermal processes or irrigation.
- Where does the remainder go? Identify the direct or indirect discharge route, permit limits and receiving system.
Design and construction checklist for a new or expanded fab
- Map every significant water use before sizing supply, storage and treatment equipment.
- Provide separate collection and equalization capacity for streams whose chemistry or contaminant load differs.
- Reserve sampling points that can verify influent, treated water, reuse water and final discharge quality.
- Design recovery systems around the quality required by the receiving application rather than pursuing one site-wide recycling number.
- Include reject water, concentrates, filter media, precipitated solids and other residuals in the waste-management plan.
- Confirm direct-discharge, pretreatment and local-permit requirements before finalizing pipe routing or treatment capacity.
- Evaluate drought, utility interruptions and source-water changes in redundancy and storage plans.
- Track water withdrawal, consumption, internal recycling and discharge as separate indicators.
- Coordinate wastewater planning with air-abatement and fluorinated-gas controls; one system does not replace the other.
- Report the measurement boundary, baseline year and operating conditions whenever a recycling result is published.
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