Gujarat Alkalies GACL Caustic Soda Flakes

    • Product Name: Gujarat Alkalies GACL Caustic Soda Flakes
    • Factroy Site: Lingwu, Yinchuan, Ningxia, China
    • Price Inquiry: sales3@liwei-chem.com
    • Manufacturer: Anhui Liwei Chemical Co,Limited
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    VTB
    Specifications
    HS Code 515901
    Product Name Gujarat Alkalies GACL Caustic Soda Flakes
    Chemical Formula NaOH
    Cas Number 1310-73-2
    Appearance White flakes
    Purity Naoh 98% min
    Chloride Nacl 0.05% max
    Iron Fe 10 ppm max
    Carbonate Na2co3 0.5% max
    Melting Point 318°C
    Boiling Point 1388°C
    Density 2.13 g/cm3
    Solubility In Water 111 g/100 mL at 20°C

    As an accredited Gujarat Alkalies GACL Caustic Soda Flakes factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing Each 50 kg HDPE woven bag with inner liner contains Gujarat Alkalies GACL caustic soda flakes, ensuring safe handling and moisture protection.
    Container Loading (20′ FCL) 20′ FCL loading: pack GACL caustic soda flakes in sealed polyethylene bags, palletize, secure, and protect from moisture.
    Shipping Caustic soda flakes are shipped in 25/50 kg HDPE or PP woven bags with moisture-proof liners, loaded into clean, dry containers. Classified as UN 1823, Class 8, Packing Group II, they require corrosion-resistant handling, ventilation, and protection from humidity and contamination during transit.
    Storage Store in a cool, dry, well-ventilated area away from moisture, water, acids, and incompatible chemicals. Keep containers tightly sealed and upright, protected from physical damage. Use impermeable flooring and ensure good drainage. Segregate from foodstuffs and oxidizers. Avoid humid conditions to prevent caking and loss of quality.
    Shelf Life Shelf life is indefinite when stored in sealed, dry conditions away from moisture and air. Proper handling ensures quality.
    Application of Gujarat Alkalies GACL Caustic Soda Flakes

    GACL caustic soda flakes are supplied as white deliquescent solids with NaOH mass fraction not less than 99.5%, sodium carbonate not more than 0.5%, and sodium chloride not more than 0.2% on a dry basis in the manufacturer certificate of analysis. The six downstream segments below represent established industrial routes where flake NaOH is dissolved into aqueous solution before process injection, with operating limits defined by the dissolution exotherm, ambient carbon dioxide absorption, and the specific kinetic requirements of each process.

    Bayer Liquor Digestion is Controlled by Flake Dissolution Rate, Not Just Bulk Alkalinity

    In Bayer digestion circuits, the primary function of caustic soda flakes is to reconstitute free alkali lost through red mud washing, desilication products, and evaporation-side carryover. The flakes are dissolved in spent liquor at 50–65°C in agitated predissolution tanks before transfer to digestion feed headers. The dissolution exotherm is 44.5 kJ/mol; uncontrolled water-to-flake addition can produce localized temperatures above 80°C, accelerating corrosion in carbon steel storage tanks and promoting carbonate pickup. The target free Na₂O concentration is set by bauxite mineralogy. Gibbsite plants operate with 140–160 g/L Na₂O at 140–160°C and 0.2–0.5 MPa; boehmite circuits require 180–240 g/L Na₂O at 200–240°C and 1.5–3.5 MPa; diaspore plants reach 220–260 g/L Na₂O at 250–270°C and 4.0–6.0 MPa. Addition ratio is therefore not a single batch percentage but a continuous free Na₂O control loop. The precipitation feed Al₂O₃/Na₂O mass ratio is maintained at 0.65–0.75, with spent liquor returning at 0.25–0.35. Caustic losses are typically 60–150 kg NaOH per tonne of smelter-grade alumina, depending on reactive silica and mud washing efficiency. The downstream process sequence includes flash letdown, sand removal, red mud thickening and washing, seed-hydrate precipitation in stirred vessels, and calcination. Terminal product types are smelter-grade alumina with Al₂O₃ not less than 98.5% and chemical-grade alumina. Compliance baseline includes pressure equipment under ASME BPVC Section VIII Division 1, process piping under ASME B31.3, environmental and energy management under ISO 14001:2015 and ISO 50001:2018, and worker exposure control under OSHA PEL 2 mg/m³ TWA and NIOSH IDLH 10 mg/m³. Operational limitations are specific: direct flake addition into high-temperature digestion liquor is avoided because localized caustic concentration above 300 g/L Na₂O can strip aluminosilicate scales and deposit them in downstream flash tanks. High-reactive-silica bauxite additionally requires lime dosing at 2–4 wt% of dry bauxite to stabilize desilication products and prevent heat exchanger scaling.

    Representative Bayer digestion operating ranges by bauxite mineralogy for low-to-moderate reactive SiO₂ bauxite
    Bauxite typeNaOH as Na₂O (g/L)Temperature (°C)Pressure (MPa)Caustic consumption (kg NaOH/t Al₂O₃)
    Gibbsite140–160140–1600.2–0.560–90
    Boehmite180–240200–2401.5–3.580–120
    Diaspore220–260250–2704.0–6.0100–150

    Within kraft bleach plants, caustic soda flakes are dissolved to 10–15 wt% sodium hydroxide and injected at the suction of a medium-consistency pump ahead of the extraction tower. The function is not bulk delignification; the white liquor loop already carries the pulping alkali. Instead, the flakes replace sodium hydroxide lost during recausticizing and maintain extraction-stage pH after chlorine dioxide delignification. Addition ratios are measured as percentage NaOH on oven-dry pulp: 1.5–2.5 wt% for oxygen-reinforced extraction, 2.0–3.0 wt% for oxidative extraction, and 1.0–2.0 wt% for pH adjustment in peroxide brightening. The extraction tower runs at 10–12% consistency, 60–80°C, and 60–120 min retention; bleached pulp is washed to residual sodium content below 0.1% on pulp to reduce brightness reversion. Compliance is defined by EPA 40 CFR Part 63 Subpart S for chemical pulp mill air emissions and the EU BAT conclusions under Commission Implementing Decision 2014/687/EU, with effluent AOX monitored after treatment. Terminal products include bleached softwood kraft pulp, bleached hardwood kraft pulp, dissolving pulp for viscose, and fluff pulp. Plant-scale equipment behavior shows that incomplete flake dissolution causes undissolved particles to accumulate in extraction tower bottom screens and accelerates washer blade wear; medium-consistency pumps with fluidizing rotors are therefore preferred over low-shear transfer pumps at the injection point.

    Does NaOH Concentration Below 16 wt% Eliminate Mercerization Benefits for Cotton Yarn?

    For cotton yarn, the mercerization effect is concentration-dependent and becomes visually and tensile-recovery insufficient when the NaOH falls below 16 wt%. The accepted window is 18–26 wt% NaOH, with the lower limit set by incomplete cellulose I-to-soda cellulose transition and the upper limit by excessive fiber swelling that reduces tensile strength recovery. GACL flakes are dissolved to 20–24 wt% and maintained at 15–20°C. The addition ratio in yarn mercerizing is approximately 0.3–0.5 kg NaOH per kg cotton at a material-to-liquor ratio of 1:8 to 1:12. Tension is controlled at 0.3–0.6 cN/dtex during immersion, with dwell time 45–90 s. After caustic impregnation, the yarn passes through recovery washing with 5–10 g/L acetic acid or dilute sulfuric acid neutralization to a residual fabric pH of 6.5–7.5; incomplete neutralization leaves residual alkali above 0.05% on dry fiber, causing yellowing and reactive dye hydrolysis. Processing equipment includes pad/vacuum impregnators, chainless mercerizing machines for knitted goods, and twist-free roller cages for yarn. Compliance is assessed through AATCC TM89-2019 for mercerization evaluation and ISO 13934-1:2013 for tensile strength retention. Sodium hydroxide recovery typically reaches 85–90% reuse. Terminal products are high-luster cotton yarn, sewing thread, mercerized woven shirting, and mercerized knitted fabrics.

    Comparative mercerization process windows by cotton substrate
    SubstrateNaOH concentration (wt%)Temperature (°C)TensionDwell time (s)
    Cotton yarn18–2415–180.3–0.6 cN/dtex45–90
    Woven fabric20–2616–20width control, 2–4% overfeed30–60
    Knitted fabric18–2218–22low tension20–45

    Batch saponification of coconut oil, palm kernel oil, or tallow uses caustic soda flakes as the primary sodium hydroxide source for triglyceride saponification or fatty acid neutralization. The flakes are predissolved to 48–50 wt% NaOH and dosed into a jacketed kettle at 70–90°C under an anchor impeller with tip speed 3–5 m/s. Stoichiometric caustic demand is calculated from the saponification value: refined coconut oil at SV 250 mg KOH/g requires approximately 0.178 kg NaOH/kg oil, while tallow at SV 195 mg KOH/g requires 0.139 kg NaOH/kg oil. Industrial practice uses a slight excess of 0.5–1.5 wt% NaOH on oil mass to drive free alkali below 0.5% in finished soap. The process sequence includes slow caustic addition over 60–120 min, boiling to separate glycerin in spent lye, and brine washing with 10–15% NaCl solution to reduce glycerol content below 0.3% in neat soap. Compliance for finished soap is tested under ISO 685:2020 for total alkali and total fatty matter, and consumer detergents fall under Regulation (EC) No 648/2004. Terminal products are soap noodles with total fatty matter 63–80%, toilet soap bars, laundry soap, and glycerin as coproduct. Plant-scale failure data show that uncontrolled flake addition when the oil phase is below 65°C creates sodium soap gel layers on the agitator shaft, increasing motor load by 30–50% and requiring manual scraping. A recirculation loop with in-line caustic injection prevents localized saponification. Batch yield variance is typically ±1.5% total fatty matter when the caustic pump is calibrated against solution density at 20°C.

    If Raw Water Methyl Orange Alkalinity Falls Below 20 mg/L as CaCO₃, Alkali Feed is Required Before Coagulation

    Low-alkalinity raw water, especially from upland reservoirs after snowmelt, lacks sufficient bicarbonate buffer to prevent coagulant pH depression. Caustic soda flakes are dissolved to 5–10 wt% sodium hydroxide and metered through a diaphragm pump into the rapid-mix basin at 1–10 mg/L NaOH to hold coagulation pH between 7.5 and 8.5 for alum or polyaluminium chloride. The addition ratio for acid neutralization is stoichiometric: 40 mg NaOH neutralizes 36.5 mg HCl, so an industrial waste stream with 50,000 mg/L acidity as HCl requires 54.8 kg NaOH per m³. Continuous pH control uses a three-term controller with static mixer injection, and flake dissolution tanks are sized for 24 h maximum storage to avoid atmospheric carbon dioxide absorption that raises sodium carbonate content above 0.5%. Compliance is defined by AWWA B501-19 for sodium hydroxide quality and NSF/ANSI/CAN 60 for drinking water treatment chemicals. The process reduces lime sludge handling when replacing hydrated lime, but caustic does not remove noncarbonate hardness; waters with sulfate or chloride hardness require parallel soda ash feed. Terminal products are coagulated and filtered drinking water, neutralized industrial effluent, and pretreated boiler makeup. The main operational boundary is that caustic feed above 15 mg/L in raw water with aluminum-based coagulants can form soluble aluminate species and increase dissolved aluminum in finished water above the 0.1–0.2 mg/L drinking water guidance range.

    Because silica sand digestion is controlled by quartz particle size and sodium hydroxide concentration, caustic soda flakes are dissolved to 25–50 wt% NaOH before being charged to a stirred autoclave with sand milled to D50 45–75 µm. The SiO₂/Na₂O molar ratio is maintained between 2.0 and 3.2, and flake consumption is 0.55–0.85 kg NaOH per kg silica sand at reactor temperatures of 150–200°C and pressures of 0.5–1.8 MPa for 4–8 h. Unmilled sand above 150 µm reduces silica conversion to below 70%, leaving undigested quartz that accelerates autoclave impeller and discharge valve wear. The resulting sodium silicate liquor is pressure-filtered and adjusted to 38–55 wt% solids. Downstream neutralization with sulfuric acid precipitates silica to customer-specific grades; sodium silicate and precipitated silica placed on the European market are registered under Regulation (EC) No 1907/2006 and classified under CLP Regulation (EC) No 1272/2008. No single horizontal product standard applies across all detergent, tire, and personal care silica grades. Terminal products include sodium silicate liquor for detergent builders, precipitated silica for tire and toothpaste formulations, and zeolite precursors for catalysts. Process safety limits require completing the exothermic flake dissolution before sand charging to avoid localized hot spots above 200°C that accelerate stress corrosion cracking in austenitic stainless steel reactors.

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    Certification & Compliance
    More Introduction

    Gujarat Alkalies and Chemicals Limited (GACL) Caustic Soda Flakes is a solid, white, deliquescent sodium hydroxide product with a minimum total alkalinity of 99.5% as NaOH on dry mass. The material is identified by molecular formula NaOH, CAS registry number 1310-73-2, molar mass 40.00 g/mol, and HS code 28151110. Under transport regulations it falls under UN 1823, Class 8, Packing Group II. The product is obtained by concentrating membrane-cell caustic liquor to molten sodium hydroxide and solidifying it as flakes on cooled flaking surfaces. It is packed in 25 kg or 50 kg woven HDPE bags with inner linear low-density polyethylene liners, or in 500–1000 kg flexible intermediate bulk containers. Because the flake is hygroscopic and reacts with atmospheric carbon dioxide, closed, moisture-excluded storage is mandatory; opened stock may develop a surface crust of sodium carbonate that alters free alkalinity.

    How Does Membrane-Grade Flake Differ in Trace Chloride and Chlorate from Diaphragm-Grade Material?

    The cell technology upstream of the evaporation stage sets trace-impurity limits. Membrane-cell caustic soda is produced through perfluorinated ion-exchange membranes that selectively transport sodium ions and reject chloride; diaphragm-cell material carries higher sodium chloride and sodium chlorate burdens. For corrosion-sensitive applications, the difference appears as chloride entering the reaction mass and as chlorate purge load in waste streams. Representative merchant-grade acceptability limits for GACL flake are summarised in the following table; individual lots may show tighter values on the certificate of analysis. Where food contact or indirect additive use is intended, the lot must also meet 21 CFR 172.880 or Food Chemicals Codex limits because technical-grade data alone are not sufficient for that regulatory status.

    ParameterTypical limitMethod reference
    Total alkalinity as NaOH, % w/w≥99.5%ASTM E291-18
    Sodium carbonate as Na2CO3, % w/w≤0.5%ASTM E291-18
    Sodium chloride as NaCl, % w/w≤0.1% for membrane-grade flake; diaphragm-grade may reach 1.0–1.5%Potentiometric titration / IS 252:2013
    Iron as Fe, ppm≤20 ppmICP-OES
    Sodium sulphate as Na2SO4, % w/w≤0.02%Turbidimetric
    Silica as SiO2, % w/w≤0.02%Spectrophotometric

    The chloride limit is not arbitrary. In a 10 m³ batch neutralisation system, a flake charge equivalent to 1000 kg NaOH with 0.1% NaCl introduces 1.0 kg chloride into the process; diaphragm-grade material at 1.5% NaCl would introduce 15 kg chloride in the same alkali mass. This difference becomes significant in closed-loop processes where chloride is not volatilised and may accumulate through evaporation. Specific long-term corrosion data for every plant configuration is limited; coupon exposure remains the accepted method to set chloride ceilings in austenitic stainless steel storage and digesting systems.

    Solid-State Handling Variability in Flake, Prill, and Lye Systems

    Flake morphology produces a larger surface area than bead-form prills, which accelerates both dissolution and moisture uptake. Bulk density of sodium hydroxide flakes is commonly in the range 0.9–1.1 g/cm³, while prilled product may occupy 1.1–1.2 g/cm³; this affects silo capacity, bridging, and feed-screw volumetric calibration. The integral enthalpy of solution of solid NaOH in water at 25°C is approximately −44.5 kJ/mol; therefore dissolution is strongly exothermic. Controlled flake addition through a rotary valve into a stirred dilution tank with external cooling or recirculation is the usual route to prevent local boiling. Rapid addition of a 250 kg flake charge into 2 m³ of water can raise bulk temperature above 80°C unless heat is removed; the actual rise depends on initial water temperature, vessel metallurgy, and mixing intensity.

    AttributeFlakePrill / pearlLye 47–50%
    NaOH concentration≥99.5%≥99%47–50%
    Water mass per 1000 kg NaOH≤5 kg≤10 kg≈1000 kg
    Freezing / caking behaviourNon-freezing; cakes above 60% RHNon-freezing; lower caking tendencyCrystallises near 10–12°C
    Dissolution handlingHigh heat of solution; vortex suppression requiredModerate dusting; conical screening may be neededLiquid dosing pump; freeze protection required
    Chloride influenceMembrane-grade ≤0.1%Membrane-grade ≤0.1%Depends on cell route

    Batch saponification for sodium soap does not require a separate header; high-assay flake alters the water balance directly. For a 10,000 kg fat charge with saponification value 195 mg KOH/g, the alkali demand is approximately 1,390 kg NaOH; the equivalent use of 50% lye would add roughly 1,390 kg water to the soap pan. The lower water input raises the boiling point of the mass, shortens the time needed to reach a specified moisture endpoint, and reduces salt-water discharge from the finishing stage. Flake is added through an alkali feeder to the hot fatty acid or neutral fat charge with agitation; local hydroxide concentration at the point of addition must be diluted by the surrounding mass to avoid colour-forming oxidation.

    When Caustic Flake Replaces 50% Lye in a Bayer Digestion Circuit

    Alumina refineries use sodium hydroxide for bauxite digestion and for restoring free caustic strength in the recirculating liquor. The mass relation between NaOH and Na2O equivalent is 1.290 kg NaOH per 1.0 kg Na2O; this conversion is used when flake additions are expressed against alumina production formulas. Low-temperature digestion near 140–150°C typically maintains free caustic from 200–250 g/L Na2O(c); high-temperature diasporic digestion near 240–260°C may require 250–280 g/L Na2O(c) depending on reactive silica and bauxite charge. Flake addition should be made to the dilute side of the circuit before heat recovery rather than into hot aluminate slurry; this avoids a high local caustic gradient that accelerates sodium alumino-silicate scale deposition on tube-side heat exchange surfaces. Low chloride flake at ≤0.1% NaCl restricts chloride concentration in the digest liquor; excess chloride can intensify pitting risk in stainless steel digest evaporators and flash tanks.

    Mercerisation and Sulfonation Process Constraints

    Textile mercerisation commonly requires NaOH concentration in the range 18–25% w/w; below 18% swelling is incomplete, while above 25% fibre stiffness and wash-water caustic load increase. High-assay flake is dissolved with cooling to produce mercerising liquor; final strength is confirmed by density measurement at 15°C or by acid titration. In detergent intermediate neutralisation, flake NaOH reacts with sulfonated alkylbenzene to form sodium sulfonate and sodium sulfate; carbonate in the flake must remain low because carbonate decomposition can generate carbon dioxide and contribute to foam in the slurry. A specification ceiling of ≤0.5% Na2CO3 is therefore applied at purchase for this application.

    Kraft and sulfite pulp mills use flake caustic as make-up chemical for white-liquor causticising and for chlorine dioxide generation. White-liquor active alkali is maintained through caustic addition after clarification; flake with low sodium carbonate is preferred because carbonate can depress effective causticising efficiency. In chlorine-containing scrubber systems, sodium hydroxide is predissolved to 20–25% before injection, and the reaction 2 NaOH + Cl2 → NaOCl + NaCl + H2O is held at pH 9.0–10.5 to convert chlorine without forming excessive chlorate. pH below 7.0 drives chlorine off-gas; pH above 10.5 can reduce hypochlorite stability in stored solution.

    Acidic wastewater neutralisation uses a 25% pre-diluted flake solution metered to a pH setpoint of 7.0–8.5. Direct flake addition to acidic wastewater is avoided because the local high pH can precipitate metal hydroxides suddenly and generate heat. Alkalinity verification is performed by ISO 9963-1 or Standard Methods 2320 B; pH control loops should include fail-closed caustic valves and mixing tanks sized for at least 10 minutes retention to prevent overshoot.

    Operational boundaries are significant. Flake sodium hydroxide is incompatible with aluminium, tin, zinc, and galvanized steel when moisture is present; the reaction can release hydrogen. Mixing with mineral acids is strongly exothermic and should be carried out by slow addition with cooling. In closed systems, sodium hydroxide must not be mixed with chlorinated solvents such as trichloroethylene or chloroform; base-promoted dehydrohalogenation can generate unstable intermediates and overpressure. Occupational exposure limits for sodium hydroxide are commonly applied as a ceiling of 2 mg/m³, and the IDLH is listed as 10 mg/m³. Bulk handling systems should be constructed of carbon steel or austenitic stainless steel, with aluminium components excluded from load cells, fasteners, and dust-contact areas. Bags should be stored indoors at relative humidity below 60%; if condensation is allowed to form, the flakes cake, carbonate, and become difficult to meter accurately.