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Ozone Water Electronic/EL Grade

    • Product Name: Ozone Water Electronic/EL Grade
    • Factroy Site: Yudu County, Ganzhou, Jiangxi, China
    • Price Inquiry: admin@ascent-chem.com
    • Manufacturer: Ascent Petrochem Holdings Co., Limited
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    Specifications
    HS Code 355778
    Product Name Ozone Water Electronic/EL Grade
    Chemical Formula O3 dissolved in H2O
    Physical State Clear liquid
    Color Colorless
    Odor Slight pungent ozone odor
    Ozone Concentration Typically 1-20 mg/L (ppm), depending on application and grade
    Ph Neutral to slightly acidic, approximately pH 5.5-7.5 at 25°C
    Density Approximately 0.998 g/cm3 at 20°C
    Electrical Resistivity High purity; base water resistivity is >=18.0 MOhm.cm at 25°C
    Total Organic Carbon Toc Less than or equal to 5 ppb typical for electronic-grade water
    Metal Impurities Controlled to sub-ppb levels per electronic/EL-grade specifications
    Particle Contamination Electronic-grade limit, for example <=1 particle/mL at >=0.1 um
    Stability Unstable; ozone decomposes to oxygen over time, so use or generation is typically in-line

    As an accredited Ozone Water Electronic/EL Grade factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing Packaged in sealed, opaque electronic-grade containers to preserve purity, available in 1-liter bottles for precise semiconductor and lab use.
    Container Loading (20′ FCL) 20′ FCL loading: Ozone Water Electronic/EL Grade is packed in sealed HDPE drums, secured upright, ventilated, and segregated for safe transport.
    Shipping Ozone Water Electronic/EL Grade is shipped in sealed, UV-resistant containers under controlled temperature to prevent decomposition. Due to its strong oxidizing nature, transport follows strict hazmat regulations. Expedited delivery is essential, with temperature-monitored logistics ensuring purity and stability from dispatch to final destination.
    Storage Store Ozone Water (Electronic/EL Grade) in sealed, ultrapure-compatible containers (quartz, PTFE, or electropolished stainless steel) away from heat, light, and organic materials. Keep cool and well-ventilated, as ozone decomposes to oxygen over time. Minimize headspace, avoid contamination, and monitor dissolved ozone concentration to maintain required purity and performance.
    Shelf Life Shelf life is very short; ozone rapidly decomposes to oxygen. Use immediately, store cold and dark, and verify concentration before use.
    Application of Ozone Water Electronic/EL Grade

    Front-end-of-line wafer preparation on 300 mm silicon has moved toward dilute ozonated ultrapure water to collapse the number of wet chemistry steps between silicon nitride spacer deposition and gate oxide formation. Electronic/EL-grade ozone water is injected into a quartz overflow bath through a membrane contactor to avoid introducing gas-phase microbubbles; the dissolved ozone concentration is held at 2.0–3.5 mg/L at 21–23 °C, with a recirculation turnover time of 60–90 s and point-of-use filtration at 0.04 μm. This corresponds to an addition ratio of 0.0002–0.00035 wt% ozone in ultrapure water, and the aqueous phase is not further diluted before contacting the wafer. The water matrix is required to satisfy ASTM D5127-13(2020) Type E-1.2 for cation/anion background, SEMI F63-0701 for ultrapure water distribution, and ISO 14644-1:2015 Class 3 for the processing environment. In the production sequence, wafers receive a dilute 0.5% HF-last etch, rinse, then enter the ozone water bath for 180–240 s while a 950 kHz megasonic transducer provides acoustic energy at 0.8–1.2 W/cm² to displace sub-65 nm particle populations. Dissolved ozone is monitored by UV photometric analysis at 254 nm. The ozone oxidizes surface organic residues and re-grows a chemical oxide of 0.7–1.0 nm; this step is used before ALD hafnium oxide or plasma nitridation. Production-scale equipment observed in this application includes 50-wafer quartz and fluoropolymer cassettes, quartz tanks with overflow weirs, and gas-phase ozone destruct units maintaining exhaust below 0.05 ppm ozone. The main processing bottleneck is dissolved ozone decay during batch idle time; at 23 °C without wafer load, decay of 0.15–0.25 mg/L per minute occurs in an open tank, requiring closed-loop generation and automatic injection. Terminal device types fabricated after this cleaning sequence include logic application-specific integrated circuits, DRAM, 3D NAND, power management ICs, and radio-frequency front-end modules where gate oxide integrity is sensitive to residual organic contamination.

    What Dissolved Ozone Loading Triggers Organic Residue Removal in Single-Wafer Post-Ash Cleaning?

    The transition from Caro’s acid or solvent-based resist removers to ozonated ultrapure water on single-wafer spray platforms is constrained by the mass-transfer limit of dissolved ozone at the wafer boundary layer. Typical process conditions for post-ash residue removal after 248 nm and 193 nm photoresist patterning use a dissolved ozone concentration of 25–50 mg/L in degassed ultrapure water, delivered through a 0.6 mm quartz nozzle at 0.3–0.5 MPa pressure to a wafer rotating at 500–1,500 rpm. The addition ratio is not expressed as a bulk bath percentage because the tool operates in a single-wafer open-bowl mode; rather, the ozone generator output is set to maintain 25–50 mg/L at the dispense point, which corresponds to roughly 0.0025–0.005 wt% dissolved ozone. Compliance in this application is anchored to SEMI S2-0718 for equipment safety and exhaust interlocks, OSHA 29 CFR 1910.1000 Table Z-1 for the 0.1 ppm eight-hour ozone exposure ceiling at operator stations, and SEMI F63-0701 for the high-purity water supply feeding the ozone contactor. Production-scale equipment behavior includes a measurable radial etch non-uniformity of 3–5% across a 300 mm wafer when the nozzle scan velocity is not synchronized with the edge bead removal zone; the outer 5 mm of the wafer frequently retains carbon-rich residue unless a second pass is programmed with a reduced dispense flow of 0.8 L/min. The downstream production process follows oxygen plasma ashing: the wafer is cooled, treated with ozone water for 60–120 s, then rinsed with hot ultrapure water at 50 °C and spin-dried under nitrogen. The terminal products in this process flow include CMOS image sensors, embedded non-volatile memory, bipolar-CMOS-DMOS mixed-signal devices, and power amplifier die where organic residue on tungsten or cobalt contacts would otherwise increase via resistance.

    Panel-Level Organic Film Removal After TFT Wet Etch in Gen 8.5 Substrate Fabs

    In TFT array fabrication for large-format liquid crystal displays and active-matrix organic light-emitting diode backplanes, electronic/EL-grade ozone water is used after wet etch of source-drain metallization and before plasma-enhanced chemical vapor deposition of silicon nitride passivation. The process typically employs a horizontal conveyorized or linear spray module with dissolved ozone maintained at 10–20 mg/L in ultrapure water at 22–25 °C, applied to 2200 mm × 2500 mm Gen 8.5 glass substrates at a line speed of 1.0–1.5 m/min. The addition ratio in this continuous process is expressed as ozone mass per liter of aqueous phase, 10–20 mg/L, which corresponds to 0.001–0.002 wt%; there is no co-solvent or surfactant added because residues would alter thin-film transistor threshold voltage stability. Compliance requirements include ASTM D5127-13(2020) Type E-1.2 or better feed water, ISO 14644-1:2015 Class 5 for the wet bench enclosure, and SEMI S2-0718 for toxic gas and ozone exhaust interlocking. Production-scale failure modes observed on fabrication lines include backside mist accumulation on the glass transfer rollers when exhaust balance drifts negative by more than 10 Pa, leading to electrostatic discharge marks on the glass edges. The downstream supply chain converts the cleaned TFT backplanes into liquid crystal display modules for televisions, monitors, notebook panels, automotive instrument clusters, and OLED smartphone displays; all finished panel types require the removal of post-etch organic contamination to prevent hillock formation in subsequent aluminum or copper wet deposition steps.

    After inline alkaline texturing of monocrystalline wafers, photovoltaic cell fabrication lines use electronic/EL-grade ozone water as a final organic removal and surface conditioning step before amorphous silicon or aluminum oxide passivation deposition. The dissolved ozone target in the inline immersion rack is usually 3–8 mg/L at 20–25 °C, with a bath residence time of 90–150 s for M10 or M12 wafer formats. Because the cleaning fluid is continuously generated from ultrapure water and oxygen gas, the addition ratio is maintained as 0.0003–0.0008 wt% ozone, and the bath is replenished at 2–3 tank volumes per hour to prevent accumulation of residual alkaline silicon etch products. Industry compliance for the water supply is commonly aligned to ASTM D5127-13(2020) Type E-2 or stricter, with cleanroom conditions at ISO 14644-1:2015 Class 6 around the wet chemistry station. Equipment on production lines includes 4000–8000 wafer-per-hour inline systems with ozone injected through a venturi contactor and residual ozone in the atmosphere controlled by a catalytic destruct unit to less than 0.05 ppm. The downstream production process proceeds immediately to rinsing, warm nitrogen drying, and PECVD of passivation layers; extended queue time after ozone water drying is limited to 2–4 h before re-contamination from volatile organics is observed. Terminal finished product types in this segment include passivated emitter and rear cell, tunnel oxide passivated contact, and silicon heterojunction solar cells, which are then assembled into glass-backsheet and glass-glass modules for utility, commercial, and residential photovoltaic installations.

    When Copper Pillar Bump Undercut Control Replaces Alkaline Flux Cleaners in Wafer-Level Packaging

    Wafer-level packaging lines with copper pillar bump pitch below 40 μm have adopted ozonated ultrapure water to remove organic flux residue and post-plating polymers without the high-pH cleaners that aggravate copper undercut and titanium-tungsten adhesion layer attack. In this application, electronic/EL-grade ozone water is dispensed at 8–15 mg/L dissolved ozone onto a spinning reconstituted wafer on tape or carrier, at 25–30 °C, for 60–120 s per pass. The addition ratio in the aqueous phase is 0.0008–0.0015 wt% ozone; it is not combined with hydroxylamine, tetramethylammonium hydroxide, or amine-based flux removers because simultaneous use accelerates copper oxide dissolution and yields non-uniform bump height across the die street. Compliance for the chemical distribution module includes SEMI S2-0718 for interlocks and exhaust, SEMI F63-0701 for ultrapure water quality, and IPC J-STD-001H for the soldering and assembly boundaries governing cleanliness after flux removal. Production-scale behavior includes a recurrent edge-fast voiding signature on organic substrates when the ozone water temperature exceeds 30 °C; below 25 °C, the residue removal rate on rosin mildly activated flux drops sharply by 40–50%, so the operating window at the dispense point is typically controlled to 26–28 °C. The downstream production process then proceeds to hot ultrapure water rinse at 50 °C, spin dry, plasma pre-clean, and under-bump metallurgy inspection by scanning electron microscopy. Terminal finished product types include copper pillar bump wafers for mobile application processors, power management integrated circuits, radio-frequency front-end modules, and chip-scale packages where flux residue left under the bump would impair thermosonic flip-chip bonding and lead to post-reflow solder joint voids.

    Replacing Sulfuric-Peroxide Mixtures in Photomask Stripping with Ozonated Ultrapure Water

    Conventional mask stripping has relied on heated H₂SO₄/H₂O₂ mixtures, but photomask and reticle cleaning for 193 nm and extreme ultraviolet lithography is shifting to ozonated ultrapure water to reduce sulfate residue and electrostatic discharge damage on absorber surfaces. The electronic/EL-grade ozone water formulation is generated at 10–20 mg/L with a pH of 4.5–5.5, applied through a point-of-use fused silica spray bar to a 6025 mask substrate rotating at 300–800 rpm for 30–90 s. The addition ratio is 0.001–0.002 wt% dissolved ozone, with no acid or oxidizer added; if molybdenum-silicon absorber stack materials are present, the process temperature is held at 20–22 °C to avoid accelerated molybdenum dissolution. Compliance references include SEMI P1 for photomask substrate requirements, ISO 14644-1:2015 Class 3 for reticle processing, and ASTM D5127-13(2020) Type E-1.2 for the rinse water feed. In production-scale reticle cleaning tools, the main bottleneck is dissolved ozone half-life in the small-bore delivery line; if the line volume exceeds 2 L and flow remains below 1 L/min, the delivered concentration at the nozzle can be 30–40% lower than the contactor setpoint due to wall-catalyzed decomposition. Downstream production processes include final rinse with ultrapure water, air-knife drying, and aerial image metrology before the reticle enters a lithography scanner or mask inspection tool. Terminal product types in this segment are binary and phase-shift photomasks, attenuated phase-shift masks, and multilayer extreme ultraviolet reticles used in semiconductor device manufacturing at nodes at or below 28 nm.

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    Certification & Compliance
    More Introduction

    In front-end wet processing, Ozone Water Electronic/EL Grade is applied as a dynamically generated ozonated ultrapure water stream, not as a stored oxidant bath. The fluid is generated from Type E-1.2 ultrapure water conforming to SEMI C63 and ASTM D5127 with resistivity maintained at 18.2 MΩ·cm at 25 °C, total organic carbon below 1 µg/L, and dissolved oxygen below 50 µg/L. Ozone is introduced from a proton-exchange membrane electrolytic generator and contacted under backpressure; the resulting stream is specified for metal contamination of not more than 0.5 µg/L per element for the 35 elements commonly screened by ICP-MS, particle counts at or below 5 particles/mL at a size threshold of 0.05 µm per SEMI F58, and dissolved ozone concentration monitored by an in-line UV analyzer referenced to SM 4500-O₃ indigo methodology. Because the first-order half-life of dissolved ozone in 18.2 MΩ·cm water at 20 °C is generally reported in the range of 20–30 min, supply beyond a local recirculation loop is not a supported configuration; the product is dispensed within a short path from the ozone contactor to the process chamber.

    Model Matrix and Delivery Pressure Ceilings

    The model suffix denotes the nominal dissolved ozone concentration at the dispense nozzle. OWE-EL-020 delivers a nominal 20 mg/L with a turndown range of 10–30 mg/L at 8–20 L/min; OWE-EL-050 delivers 50 mg/L with 20–70 mg/L turndown at 12–30 L/min; OWE-EL-100 delivers 100 mg/L with 30–120 mg/L turndown at 15–40 L/min. For all three, the contactor outlet pressure is maintained between 200 kPa and 400 kPa. Below 200 kPa, gas-liquid mass transfer becomes unstable and dissolved ozone variability can exceed ±3 mg/L. Above 400 kPa, the risk of gas carryover into the dispense line increases, with bubble counts exceeding 10 bubbles/mL measurable by an acoustic bubble meter. Point-of-use filters are PFA-housed 0.05 µm rated membranes; pressure drop across the filter is specified at <70 kPa at 20 L/min and 22 °C.

    Output matrix for Ozone Water Electronic/EL Grade at a feed temperature of 22 ± 1 °C
    ParameterOWE-EL-020OWE-EL-050OWE-EL-100
    Nominal dissolved O₃20 mg/L50 mg/L100 mg/L
    Dispense flow range8–20 L/min12–30 L/min15–40 L/min
    O₃ turndown range10–30 mg/L20–70 mg/L30–120 mg/L
    Contactor outlet pressure200–400 kPa
    Particle specification, ≥ 0.05 µm5 particles/mL by SEMI F58
    Metal contamination, per element0.5 µg/L by ICP-MS

    Analytical verification at point of use is performed by automated sampling through PTFE or PFA sample lines. Metal cations are determined by ICP-MS after direct injection into a cleanroom-compatible instrument with a detection limit below 0.05 µg/L for target transition metals. Anion contaminants are measured by ion chromatography with suppressed conductivity detection, with reporting limits below 0.1 µg/L for chloride, sulfate, nitrate, and phosphate. Dissolved ozone concentration is verified by the SM 4500-O₃ indigo colorimetric method and correlated with an in-line UV analyzer at 258 nm. The analyzer is challenged daily with a 50 mg/L reference solution and must agree within ±3% before lot release.

    PFA and PTFE fluid paths are mandatory for all wetted components from contactor outlet to dispense nozzle. Field teardown data from 300 mm wet-bench installations indicate that stainless-steel fittings, even at low surface roughness, become a metal contamination source within 200–400 h of intermittent ozonated water exposure. Elastomer seals are excluded after the ozone injection point; fluoropolymer O-rings are used instead. The product is not compatible with amine-containing chemical additives because dissolved ozone reacts rapidly with ammonia and secondary amines, producing nitrate and organic by-products that elevate TOC above the 1 µg/L base level. Operational boundary: when feed water temperature exceeds 25 °C, the dissolved ozone concentration at the dispense nozzle decreases by approximately 6–8% per °C; therefore process recipes based on 50 mg/L must be revalidated if the UPW plant operates above 25 °C.

    What Distinguishes EL-Grade from Commodity Ozone-Water Mixtures?

    The principal distinction is the combination of electrolytic ozone generation and point-of-use purity controls. Commodity ozonated water produced by corona discharge from oxygen can entrain nitrogen oxides and may require an additional catalyst bed; residual nitrate and nitrite can elevate anion loading to 5–20 µg/L, which exceeds front-end cleaning budgets. EL-grade ozonated water generated from a proton-exchange membrane electrolytic cell does not introduce nitrogen-based gas impurities. In addition, commodity systems often use 316L stainless steel gas manifolds and contactors, which release iron and chromium at low ppb levels under aqueous ozone exposure. The EL-grade product specifies no metallic wetted surfaces downstream of the generator. Differences are also expressed in dissolved hydrogen peroxide and ozone decay rate: corona-derived streams can contain residual hydrogen peroxide from gas-phase chemistry, whereas the electrolytic cell path generates ozone in the aqueous phase with comparatively lower peroxide background.

    Comparative matrix for oxidant streams used in front-end cleaning
    ParameterEL-Grade Ozone WaterCommodity Ozone-WaterHot Sulfuric Peroxide
    Primary oxidantAqueous O₃Aqueous O₃ plus NOₓ/H₂O₂H₂SO₄/H₂O₂
    Operating temperature18–25 °C18–30 °C100–140 °C
    Metal contamination0.5 µg/L per element1–10 µg/L due to stainless steel componentsVariable, often >10 µg/L depending on chemical grade
    Particle count, ≥ 0.05 µm5 particles/mL10–100 particles/mL typicalNot usually specified for particles at dispense
    Residual contamination after rinseNone; volatile oxygenNitrate/nitrite residues possibleSulfur residues requiring hot UPW rinse
    Compatibility with porous low-kAcceptable within time limitsSimilar to EL-grade but less controlledPotential carbon depletion and pore damage

    Primary application data from single-wafer cleaning tools show that a 20–50 mg/L dose at 22 °C oxidizes organic surface contaminants without the thermal budget of hot sulfuric peroxide. For post-etch residue removal on damascene copper lines, exposure times of 30–120 s at 50 mg/L reduce carbon-containing residue thickness by 40–80%, but the reduction is geometry-dependent; tight-pitch metal lines with aspect ratios above 3:1 show a decrease in cleaning uniformity because ozone diffusion into the cavity is slower than surface consumption. In pre-ALD oxide formation, immersion in 50–100 mg/L ozonated UPW at 25 °C for 60–180 s produces a hydrophilic chemical oxide layer; ellipsometric thickness is commonly below 1.2 nm. Published data for exact oxide thickness on patterned structures is limited and should be verified by inline ellipsometry.

    Electrolytic ozone cell output drifts with anode coating condition. Field data from production units show that after 6,000–8,000 h of operation at 60–80% duty cycle, cell current demand at constant ozone output can increase by 10–15%. Maintenance intervals for the cell stack and deionizer cartridges are set at 4,000 h or 12 months, whichever occurs first. Oxygen evolution at the anode must be separated efficiently; carryover of oxygen reduces the dissolved ozone concentration by dilution and can cause flow pulsation in downstream pumps. At nominal 50 mg/L, the observed short-term coefficient of variation is 2.1% within a single 25-wafer FOUP run and 4.7% across an 8 h shift, with variation dominated by feed water temperature drift and membrane hydration state.

    When High-Aspect-Ratio Structures Are Cleaned with Ozone Water

    Mass-transfer limitations become the controlling factor at aspect ratios above 3:1. Dissolved ozone is consumed at the wafer surface faster than diffusion replenishes the liquid inside trenches or vias. In patterned structures with 40–60 nm half-pitch, the local dissolved ozone concentration at the bottom of a 2 µm deep trench can be 30–50% lower than the bulk liquid concentration. This concentration gradient produces non-uniform organic removal and can leave carbon-bearing residues near the bottom sidewall. Process compensation includes raising the bulk ozone concentration to 80–100 mg/L or increasing the dispense flow rate to maintain fluid turnover at the wafer surface above 10 L/min. However, at 100 mg/L the dissolved ozone can etch certain resists or generate excessive surface oxidation. Process engineers should set the ozone concentration based on the limiting feature geometry rather than blanket wafer tests.

    Waste streams from ozone water are treated by UV irradiation at 254 nm or catalytic destruction before discharge because municipal wastewater permits typically require dissolved ozone below 0.1 mg/L. The waste line must be sized for the maximum dispense flow plus rinse water; backpressure in the drain can cause ozone gas breakout and odour control must comply with occupational exposure limits of 0.1 ppm over an 8 h time-weighted average in the process bay. Material for drain piping should be PVDF or polypropylene; CPVC and PVC are acceptable for short runs but should be assessed for oxidative embrittlement at continuous ozone exposure above 5 mg/L.

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