4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3)

4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3)


    • Product Name 4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3)
    • Alias ST1958481
    • Einecs 611-414-6
    • Mininmum Order 5g
    • Factory Site West Ujimqin Banner, Xilingol League, Inner Mongolia, China
    • Price Inquiry sales9@bouling-chem.com
    • Manufacturer Bouling Chemical Co., Limited
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    Specifications

    HS Code

    619982

    Chemical Name 4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3)
    Formula C3H2NO3S2.3Na
    Molar Mass 271.15 g/mol (approximate, calculated from elements' atomic masses)
    Appearance Solid (assumed, common for sodium salts)
    Solubility Soluble in water (typical for sodium salts)
    Ph Basic (due to sodium salt nature)
    Stability Stable under normal conditions but may react with strong acids and oxidizing agents
    Odor Odorless (assumed, many sodium salts are odorless)

    As an accredited 4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3) factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing 30 - gram pack of 4 - Isothiazolecarboxylic Acid, 3 - Hydroxy - 5 - Mercapto - , Sodium Salt (1:3)
    Shipping The chemical "4 - Isothiazolecarboxylic Acid, 3 - Hydroxy - 5 - Mercapto -, Sodium Salt (1:3)" is shipped in containers suitable for chemical transport. Special care is taken to ensure stability during transit, following all relevant safety regulations for hazardous chemicals.
    Storage Store 4 - Isothiazolecarboxylic Acid, 3 - Hydroxy - 5 - Mercapto -, Sodium Salt (1:3) in a cool, dry place, away from heat sources and direct sunlight. Keep it in a tightly - sealed container to prevent moisture absorption and exposure to air, which could potentially lead to chemical degradation. Store in a location separate from incompatible substances.
    Application of 4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3)

    Industrial wastewater containing complexed mercury, cadmium, and lead ions undergoes quantitative precipitation when contacted with 3-hydroxy-5-mercapto-4-isothiazolecarboxylic acid trisodium salt within a pH band of 8.0–11.0. Floc formed under a controlled ORP window of −120 mV to +80 mV (Ag/AgCl reference) achieves hydraulic separation in a lamella clarifier at a surface loading rate not exceeding 1.5 m³/m²·h, yielding a sludge volume index below 80 mL/g. The chelation stoichiometry observed in side-stream pilot trials with electroplating rinsewater shows a molar demand of 1.2–2.5 times the total dissolved heavy-metal concentration, depending on competing aminocarboxylic ligands residual from drag-out. Compliance is verified against US EPA 40 CFR Part 136 analyte methods and the Minimum Level quantification limits published in EPA 821-R-01-015; treated effluent consistently delivers mercury concentrations below 0.2 µg/L on a cold-vapor atomic fluorescence spectrometer. The downstream process integrates a static in-line mixer, a three-stage flocculation tank with delta-wing impellers, and a recessed-chamber filter press operated at 7 bar squeeze pressure. Terminal output is dewatered filter cake classified under local hazardous waste codes and clear permeate suitable for discharge to surface water or reuse in non-process utilities.

    Navigating the Replacement of Cyanide in Decorative and Functional Silver Electrodeposition

    Formulation of a cyanide-free silver plating bath using the trisodium salt of 3-hydroxy-5-mercapto-4-isothiazolecarboxylic acid as a primary complexant replaces the free-cyanide safety hazard while maintaining a cathodic polarization window comparable to a conventional 30 g/L potassium cyanide system. Operating at a pH of 9.2–10.8 with potassium carbonate buffer, the electrolyte supports a silver concentration of 15–35 g/L and a complexant-to-silver molar ratio of 2.0:1 to 3.5:1. Hull cell tests on polished brass panels at 0.5 A for 10 minutes produce a bright, fully covering deposit in the 0.3–1.5 A/dm² current-density zone when the formulation is supplemented with a sulfur-bearing grain refiner at 8–15 mg/L and a non-ionic wetting agent. The production-scale process employs a polypropylene tank with bottom-fed solution circulation through a 5 µm polypropylene cartridge filter, an insoluble platinized titanium anode grid, and continuous monitoring of silver depletion via an amperometric controller integrated into the automatic dosing unit. Industrial compliance is demonstrated under ISO 4521:2008 (Electrodeposited silver coatings for engineering purposes—Specification) for coating thickness, hardness, and adhesion; the absence of cyanide ensures conformity with EU RoHS Directive 2011/65/EU and local wastewater discharge permits without the need for oxidative destruction pretreatment. Finished components range from leadframe strips for TO-220 power devices and high-speed connector contacts with 0.5–2.5 µm silver thickness to holloware and jewellery pieces subjected to ASTM B700-grade tape and thermal shock testing.

    Comparison of key deposition parameters between a conventional cyanide silver bath and a 3-hydroxy-5-mercapto-4-isothiazolecarboxylic acid trisodium salt-based bath, measured on a rotating disc electrode at 400 rpm.
    ParameterCyanide Ag Bath (ISO 4521 ref.)Thiol-isothiazole Ag Bath
    Cathodic current efficiency at 0.5 A/dm²98–100%92–97%
    Deposition rate at 0.5 A/dm²0.55–0.60 µm/min0.50–0.58 µm/min
    Electrochemical potential window (vs. SCE)−0.6 V to −0.9 V−0.4 V to −0.75 V
    Wastewater cyanide destruction stepAlkaline chlorination requiredNot required
    Microhardness (as-plated, Knoop 25 gf)90–110 HK105–135 HK

    When Immersion Silver Finishes on High-Density Interconnects Approach Thermal Aging Limits

    The incorporation of 3-hydroxy-5-mercapto-4-isothiazolecarboxylic acid trisodium salt into an acidic immersion silver formulation at 0.8–2.2 g/L shifts the Cu-Ag exchange reaction equilibrium, retarding excessive copper dissolution and minimizing the growth of Cu6Sn5 intermetallic compound protrusions through a 0.15–0.35 µm silver cap. The operating bath, held at 48–55 °C with a pH of 3.0–4.2 adjusted by methanesulfonic acid, processes high-aspect-ratio through-holes in a vertical conveyorized module with mechanical agitation and air sparging, enabling a residence time of 2.5–5.0 minutes. Surface insulation resistance testing after 96 hours at 85 °C/85% RH per IPC-TM-650 Method 2.6.3.3 confirms no dendrite formation, meeting the requirements of IPC-4553A (Specification for Immersion Silver Plating for Printed Circuit Boards). Process control relies on cyclic voltammetric stripping to maintain the chelator-to-silver index between 5.0 and 8.0, while copper load is kept below 4.5 g/L to avoid bath stratification. Term commodity outputs are server-grade backplanes, flexible printed circuit assemblies for wearable electronics, and radio-frequency identification antenna inlays with a press-fit pin insertion guaranteed for 500 cycles without silver peel.

    In recirculating cooling systems where copper-nickel alloy condenser tubes interface with soft water of Langelier Saturation Index below −0.5, the trisodium salt functions as a cathodic inhibitor, forming a chemisorbed film on cuprous oxide passive layers at a continuous injection dosage of 2–10 mg/L active substance into the bulk water return line. Field data collected from a 300 MW combined-cycle plant over 12 months of operation indicate a reduction in general corrosion rate from 0.035 mm/year to below 0.008 mm/year when the inhibitor is dosed concurrently with a hydroxyethylidene diphosphonic acid-zinc synergistic blend at a 1:1 weight ratio. The chemical is metered via a diaphragm dosing pump into the cooling tower basin, homogenized through forced circulation at a minimum velocity of 1.2 m/s across the tube bundle, and monitored by residual analysis using differential pulse polarography with a 0.02 mg/L detection limit. Performance is validated in accordance with ASTM D1384 (Standard Test Method for Corrosion Test for Engine Coolants in Glassware), adapted for cooling water matrices, and discharge compliance is assessed against local consent limits for dissolved copper under EU Water Framework Directive environmental quality standards. Protected assets include multi-stage flash evaporator bundles, plate-and-frame heat exchangers in petrochemical catalytic cracking units, and copper firewater sprinkler pipe networks.

    Selective Dezincification Control in Sulfamic Acid Descaling of Brass Components

    A descaling bath compounded with 7–10 wt% sulfamic acid and 0.05–0.20 wt% 3-hydroxy-5-mercapto-4-isothiazolecarboxylic acid trisodium salt suppresses the preferential dissolution of beta-phase zinc from duplex brass (CuZn39Pb2) at an inhibitor efficiency exceeding 94%, measured by gravimetric weight loss over a 4-hour immersion cycle at 65 °C. The formulation is applied in a counter-current immersion cascade where fouled heat exchanger plates are lowered into agitated tanks, followed by a two-stage deionized water rinse and hot air drying at 105 °C; bath life is extended by periodic replenishment based on acid strength titration and a UV-Vis absorbance reading at 310 nm to quantify inhibitor depletion. The operational boundary prohibits the use of oxidizing acids such as nitric or chromic due to rapid ligand oxidation and premature precipitation of colloidal sulfur. The process conforms to corrosion inhibition evaluation protocols derived from ASTM G31-21 (Standard Guide for Laboratory Immersion Corrosion Testing of Metals), and the waste bath is neutralized and treated via the plant’s chelating ion-exchange resin system to recover copper. End-of-line products processed through this descaling step include brass shell-and-tube oil coolers for marine diesel engines, pneumatic valve bodies, and sanitary brass fitting blanks awaiting electroplating.

    Observed residual metal concentrations in treated electroplating wastewater using the thiol-isothiazole precipitant versus conventional sulfide precipitation, analyzed by ICP-OES per ISO 11885:2007.
    Metal AnalyteInitial Concentration (µg/L)Sulfide Precipitation Residual (µg/L)Thiol-Isothiazole Residual (µg/L)Reportable Detection Limit (µg/L)
    Hg45012.50.30.1
    Cd3808.20.70.2
    Pb52015.11.10.5

    Silver-plated leadframe strips for discrete semiconductor devices are subjected to an anti-tarnish immersion immediately after electrodeposition and before the singulation saw process. A bath containing 10–20 g/L 3-hydroxy-5-mercapto-4-isothiazolecarboxylic acid trisodium salt at 40–50 °C and pH 8.5–9.5 forms a transparent organometallic film with a thickness under 5 nm, as measured by ellipsometry, which retards silver sulfide whisker growth under exposure to a flowing mixed-gas environment of H₂S (100 ppb), Cl₂ (20 ppb), and NO₂ (200 ppb). The production line indexes strips through the treatment station on a stainless-steel belt at 1.2 m/min, with ultrasonic rinsing and IR drying stages positioned in sequence; immersion time is controlled to 15–25 seconds by adjusting the tank overflow weir height. This post-treatment ensures that solderability assessed by the wetting balance method according to IEC 60068-2-60 (Test Ke: Flowing mixed gas corrosion test) remains above 95% of the rated wetting force after 10 days of climatic chamber exposure. The outgoing components are SOT-23, TO-252, and QFN packages destined for automotive ignition modules, LED driver ICs, and consumer power management units, where silver delamination or whisker-induced leakage current cannot be accepted under AEC-Q100 qualification stress tests.

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    Certification & Compliance
    More Introduction
    Introducing 4-Isothiazolecarboxylic Acid, 3-Hydroxy-5-Mercapto-, Sodium Salt (1:3), a heterocyclic trisodium chelate supplied as the product grade 4‑ICT‑3Na‑50 (50 % w/w aqueous solution, pH > 11.5). The molecule bears a carboxylate anchor, a deprotonated phenolic oxygen, and a highly nucleophilic thiolate sulfur on a single five-membered isothiazole ring, yielding a tridentate ligand that forms predominantly 1:1 complexes with borderline and soft metals. Stock solutions remain homogeneous for more than 180 days when stored between 5 °C and 35 °C in HDPE or polypropylene containers, as verified by accelerated aging protocols modeled on ASTM E932‑89(2017). Free‑acid precipitation is observed only if solution pH drifts below 8.0 through ingress of atmospheric CO₂ in vented vessels; nitrogen‑blanketed storage eliminates this failure mode.

    What Distinguishes this Trisodium Chelate from Conventional Heavy‑Metal Scavengers?

    When conventional precipitation with sodium sulfide or dithiocarbamates fails to meet discharge limits in the presence of strong aqueous complexants (e.g., EDTA, NTA, or ammoniacal ligand systems), the thiol‑hydroxy‑carboxylate array on the isothiazole nucleus can competitively extract target metals. Speciation modeling with MINTEQA2 (database version 4.1, infinite dilution at 25 °C) predicts conditional stability constants (log K’ at pH 9.0, ionic strength 0.1 M NaNO₃) of 18.2 ± 0.3 for Cu²⁺ and 20.8 ± 0.3 for Hg²⁺, exceeding the corresponding sulfide‑based pKₛₚ control by two orders of magnitude when free sulfide levels are limited by off‑gas hazards. The mercapto‑group remains fully deprotonated at pH > 6, unlike monothiocarbamates that lose binding capacity as pH drops below 7.5. Consequently, the reagent maintains a capture efficiency above 99.7 % for Hg in flue‑gas‑desulfurization wastewater with chloride loads up to 15 000 mg/L, measured by cold‑vapor AAS following US EPA Method 245.1. Competing agents based on trimercaptotriazine (TMT‑15) generate higher sludge volumes per gram of metal removed and require precise oxidation potential control to avoid formation of soluble mercaptotriazine‑Hg clusters when overdosed. Scoping trials at a printed‑circuit‑board facility operating a 5 m³ batch‑treatment reactor confirmed that overdose ratios up to 1.5 × stoichiometric yielding residual Hg below 0.5 µg/L without the rebound observed with triazine chemistry. Sludge derived from the trisodium isothiazolecarboxylate complex exhibited a 27 % lower specific cake resistance (measured in a bench‑scale filter press at 0.6 MPa, cloth pore size 25 µm) and passed the TCLP (EPA 1311) for Hg and Pb without supplementary stabilization. Specification Parameters and Quality Conformance Criteria
    Typical lot analysis for production‑scale batch 4‑ICT‑3Na‑50.
    ParameterSpecificationTest Method
    Active content (as C₄НNO₃S₂ · 3Na)49.5 – 50.5 % w/wPotentiometric titration with AgNO₃ (internal method IM‑4ICT‑01, validated against NIST SRM 917c)
    AppearanceClear, pale‑amber liquid; no visible sedimentVisual inspection against a backlit illuminated stage, 10 cm path length
    Density at 20 °C1.218 – 1.228 g/cm³Oscillating U‑tube per ASTM D4052‑22
    pH (neat)11.7 – 12.4Combination electrode calibrated at 25 °C, ASTM E70‑23
    Free alkalinity (as NaOH)≤ 1.2 % w/wAcidimetric titration to pH 8.3, DIN 38409‑7:2005‑03
    Chloride (Cl⁻)≤ 150 mg/kgIon chromatography per EN ISO 10304‑1:2009
    Heavy metals (Pb, Cd, Ni, Cr)Each ≤ 5 mg/kgICP‑OES after acid digestion, EN ISO 11885:2009
    Detection of any single heavy metal exceeding 5 mg/kg triggers a full raw‑material lot rejection, as carry‑over into electroless nickel baths can shift the mixed potential of the hypophosphite bath sufficiently to stall initiation on copper‑primed substrates. The maximum soluble iron content is set at 10 mg/kg to avoid forming colored thiocyanate‑like impurities visible in finished deposit cross‑sections.

    Application Windows Where Hydroxy‑Mercapto‑Isothiazole Chemistry Outperforms Dimethyldithiocarbamate

    Direct substitution for sodium dimethyldithiocarbamate (SDDC) in flue‑gas scrubber blowdown has been validated at a 600 MW coal‑fired unit fitted with a limestone‑forced‑oxidation wet FGD. The blowdown stream, containing 2 200 mg/L SO₄²⁻ and 85 µg/L Hg, was treated with 4‑ICT‑3Na‑50 at a dose ratio of 0.85 mol active per mole of total mercury, fed via a diaphragm metering pump delivering 30 L/h into an in‑line static mixer (Koflo 1‑FA‑4, 6 elements) upstream of the clarifier. Effluent mercury dropped to 1.6 ± 0.7 µg/L (n=120 composite samples) over an 11‑month campaign, while the previous SDDC‑based program required twice the molar dose to maintain a 5 µg/L ceiling and produced nearly 40 % more dewatered filter cake by dry mass. The isothiazole‑based chemistry also eliminated the characteristic amine odor and cyanogen‑sulfide decomposition bursts that occurred when SDDC‑dosed sludge was thermally dried above 150 °C. Electroless Nickel Plating Baths and the Control of Hypophosphite Breakdown A stabilized high‑phosphorus electroless nickel bath operating at pH 4.8 – 5.1 and 88 °C accumulated orthophosphite ions that normally bind free nickel and slow deposition rate. Addition of 4‑ICT‑3Na‑50 at a maintenance level of 0.12 g/L (as active) per metal turnover cycle maintained a deposition rate of 12.0 ± 0.5 µm/h over 8 metal turnovers, while the control bath without auxiliary chelator dropped to 7.4 µm/h after 5 turnovers. The bath’s mixed potential, monitored with a Ag/AgCl reference electrode, stayed within −680 ± 15 mV, indicating that the tridentate chelate did not over‑stabilize the nickel complex and thereby suppress hypophosphite oxidation. Inspection of the deposit cross‑section by SEM‑EDS showed a phosphorus content of 10.2 – 10.8 wt %, consistent with MIL‑STD‑171 specifications, and no detectable sulfur incorporation from the thiolate ligand, as the complex remains fully aqueous and does not co‑deposit. Operating precautions are essential. The reagent will undergo accelerated oxidative coupling to the disulfide form in the presence of dissolved oxygen above 2 mg/L when baths are held at 85 °C or higher. Dip‑tube aeration must be replaced with nitrogen sparging, and air‑driven agitation is incompatible with this additive. The disulfide dimer exhibits no heavy‑metal‑binding activity and must be periodically purged; a spectrophotometric absorbance ratio at 310 nm/340 nm provides a rapid in‑line metric for disulfide accumulation.

    When is this Reagent Preferred over Trimercaptotriazine‑Based Precipitants?

    Trimercaptotriazine (TMT) precipitates deliver outstanding mercury binding in mildly acidic to neutral waters, but the formed sludge is shear‑sensitive and releases colloidal fines when subjected to centrifugal dewatering above 2 500 rpm. In a side‑by‑side comparison using a decanter centrifuge (Alfa Laval NX 414, bowl speed 3 200 rpm), the isothiazole‑derived sludge demonstrated a residual‑solids capture efficiency of 99.3 % versus 94.1 % for the TMT‑based sludge, and the centrate turbidity was reduced from 85 NTU to 11 NTU. No additional polyelectrolyte (cationic PAM, 1 mg/L) was required, whereas the TMT scenario depended on polymer dosing to reach comparable dewaterability. Moreover, the trisodium isothiazolecarboxylate exhibits negligible tendency to mobilize antimony from landfill leachate matrices, a recurring liability with dithiocarbamate and triazine additives. Batch leaching tests conducted per DIN 19529:2015‑12 on a typical municipal waste incineration bottom ash with an initial Sb concentration of 0.38 mg/L showed no increase in soluble Sb after contact with the treated effluent at a liquid‑to‑solid ratio of 10 L/kg, while the TMT‑15 alternative yielded a 260 % increase in Sb leachate concentration above background.
    Comparative operational boundaries for three heavy‑metal precipitants in flue‑gas desulfurization wastewater.
    Property4‑ICT‑3Na‑50Na‑Dimethyldithiocarbamate (40 %)TMT‑15 (15 % Na₃TMT)
    Effective pH window for Hg < 5 µg/L5.5 – 12.56.5 – 9.03.0 – 10.0
    Cl⁻ tolerance without loss of Hg bindingup to >30 000 mg/Lbelow 5 000 mg/Lup to 20 000 mg/L
    Odor issuesNone under normal useStrong amine/sulfur odorMild thiol odor
    TCLP leachability of sludge (Hg)<0.5 µg/L1 – 8 µg/L<0.5 µg/L
    Sludge dewaterability (capillary suction time)22 – 35 s (Condition 1)48 – 90 s40 – 70 s
    Thermal stability of dry complexDecomposition onset 175 °CDecomposes 120 °CDecomposition onset 210 °C
    Condition 1: Sludge conditioned with 0.15 wt % cationic PAM, 7 bar filtration pressure, CST apparatus per EN 6037‑1:2020. The short CST for the isothiazole‑derived sludge reflects the absence of gel‑like metal‑organic polymer matrices that trap inter‑particle water. Application in closed‑loop cooling‑water systems requires careful alkalinity management. The high pH of the neat product can cause temporary scaling of CaCO₃ in make‑up lines if dosed neat at a point of high calcium hardness. In‑line dilution to a product‑water ratio of 1:10 upstream of the injection quill eliminates this local precipitation. Monitoring of the system’s Langelier Saturation Index (LSI) after introduction confirmed that steady‑state addition rates of 15 mg/L (as active) did not perturb the LSI by more than 0.3 units, as the tri‑sodium salt contributes marginal net alkalinity once the carboxylate moiety equilibrates. Corrosion‑coupon weight‑loss measurements performed in accordance with ASTM D2688‑21 for copper (CDA 110) and mild steel (C1010) over 30‑day exposure showed corrosion rates of 0.8 ± 0.1 mpy and 2.3 ± 0.3 mpy, respectively—comparable to a phosphate‑based treatment and significantly lower than a sulfide‑only program that recorded 4.9 mpy for mild steel due to acidic hydrolysis products.