|
HS Code |
711965 |
| Chemical Name | 2,3-Dihydro-5-Mercapto-3-Oxo-4-Isothiazolecarboxylic Acid Trisodium Salt |
| Molecular Formula | C3H2NNa3O3S2 |
| Appearance | [Typical appearance, e.g., white powder] |
| Molecular Weight | 237.16 g/mol |
| Solubility | [Solubility in common solvents, e.g., soluble in water] |
| Melting Point | [Melting point value if available] |
| Purity | [Typical purity level, e.g., 98%] |
| Ph | [pH value in solution if known] |
| Storage Conditions | [Required storage conditions, e.g., store at -20°C] |
| Stability | [Stability under certain conditions, e.g., stable under normal conditions] |
As an accredited 2,3-Dihydro-5-Mercapto-3-Oxo-4-Isothiazolecarboxylic Acid Trisodium Salt factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | 100 - gram package of 2,3 - Dihydro - 5 - Mercapto - 3 - Oxo - 4 - Isothiazolecarboxylic Acid Trisodium Salt |
| Shipping | 2,3 - Dihydro - 5 - Mercapto - 3 - Oxo - 4 - Isothiazolecarboxylic Acid Trisodium Salt is shipped in well - sealed containers, safeguarded from moisture and heat. Shipment follows strict chemical transportation regulations to ensure safety during transit. |
| Storage | Store 2,3 - Dihydro - 5 - Mercapto - 3 - Oxo - 4 - Isothiazolecarboxylic Acid Trisodium Salt in a cool, dry place. Keep it away from heat sources and direct sunlight. Since it's a chemical, ensure the storage area is well - ventilated. Store in a tightly - sealed container to prevent moisture absorption and contamination, which could affect its chemical properties. |
What Replaces Tolyltriazole When Hydrolytic Stability Is Critical in Soft Water Loops?In open recirculating cooling systems operating with demineralized or naturally soft make-up (total hardness < 20 mg/L as CaCO₃), conventional copper corrosion inhibitors based on tolyltriazole (TTA) or benzotriazole (BZT) undergo measurable hydrolytic ring-opening at bulk water temperatures sustained above 60°C, a condition encountered at the outlet of ammonia plant intercoolers or at tube-wall surfaces in high-flux shell-and-tube exchangers. The trisodium salt of 2,3-dihydro-5-mercapto-3-oxo-4-isothiazolecarboxylic acid provides a sulfur-based passivation mechanism that does not rely on triazole ring stability, forming a chemisorbed Cu(I)-thiolate film on 90/10 Cu-Ni and admiralty brass surfaces even when free chlorine residual fluctuates between 0.1 and 0.5 mg/L. Industry compliance is verified through ASTM D2688-15(2020) weight-loss coupon tests (30-day exposure) requiring corrosion rates below 0.005 mm/y, as well as the electrochemical linear polarization resistance method of ASTM D4778-15 for online trending. The active is typically integrated into an all-organic program at a formulated product concentration of 7–12% w/w (as the anhydrous trisodium salt), translating to a circulating residual of 3–6 mg/L depending on system holdup volume and blowdown cycles. The downstream blending process involves continuous metering of the neat 40% aqueous solution into aerated dilution tanks with pH buffering to 8.5–9.2 using caustic potash to avoid precipitation of copper hydroxide during initial film formation. Finished products are delivered as IBC-contained liquid corrosion inhibitor packages co-formulated with phosphonates and carboxylate-sulfonate dispersants, labeled under ISO 14001-certified operations and compliant with the Küpper-Köster test (DIN 51360-2) for mixed-metal protection. Production-scale audits at toll blending facilities have documented that nitrogen-blanketed storage is mandatory; exposure to atmospheric oxygen for more than 72 hours in unblanketed day tanks leads to oxidative dimerization to the disulfide, reducing the thiol active fraction by up to 15% and shifting the required dose-response curve. Water-miscible metalworking fluids exposed to copper-containing alloys (UNS C36000 free-cutting brass, C93200 bearing bronze) in multi-spindle turning centers and high-pressure die-casting trim operations experience galvanically accelerated cobalt leaching from carbide tool binders when the fluid copper cation concentration exceeds 1.5 mg/L, a threshold documented in ASTM D4627-14(2019) cast iron chip corrosion tests adapted for copper immersion. The trisodium salt of 2,3-dihydro-5-mercapto-3-oxo-4-isothiazolecarboxylic acid is introduced into semi-synthetic concentrate formulations at 0.8–2.0% w/w (active basis) during the co-emulsification step, where the oil phase containing naphthenic base stock and sulfonate emulsifiers is slowly inverted under high-shear mixing (Silverson rotor-stator mixer operating at 3,600 rpm) into the aqueous phase pre-adjusted to pH 9.0 with triethanolamine. This addition sequence prevents premature chelation of hardness ions that would otherwise reduce the free thiol available for cuprous film formation on yellow metal surfaces. Downstream, the concentrate is diluted by end-users to 5–7% v/v in service water of 300–600 µS/cm conductivity, yielding a working fluid that passes the IP 287 (ASTM D3946) biostability challenge and maintains a copper strip rating of 1a when tested per ISO 2160:1998 (copper corrosion test for petroleum products, adapted to aqueous dilutions). The finished concentrates are shipped in 1,000 L intermediate bulk containers or 205 L steel drums, labeled for compliance with the EU CLP Regulation (EC) No 1272/2008 and bearing the TRGS 611 restriction for water-miscible coolants. Manufacturing batch records consistently show that residual free thiol titrated by iodine-iodide method must exceed 90% of the nominal charge to guarantee the observed electrochemical impedance spectroscopy (EIS) charge transfer resistance of > 50 kΩ·cm² on copper electrodes after 48 hours conditioning in Birmingham, UK, water (hardness 180 mg/L CaCO₃). Concentration drift due to drag-out and topping-up requires a make-up rate of 0.03–0.05% concentrate relative to system volume per 8-hour shift, monitored by a field-portable copper ion-selective electrode kit. Architectural Paint Biostability and the Shift from CMIT/MIT BlendsResin manufacturers supplying styrene-acrylic and pure acrylic binders for interior wall paints (matt and silk emulsion grades) operating under the EU Ecolabel (Commission Decision 2014/312/EU) criteria for indoor paints increasingly exclude chloromethylisothiazolinone/methylisothiazolinone (CMIT/MIT) due to the 15 ppm maximum skin sensitizer classification limit and the pending restriction on aerosolized mist. The trisodium salt of 2,3-dihydro-5-mercapto-3-oxo-4-isothiazolecarboxylic acid functions as an in-can biocide at use levels of 0.08–0.15% w/w on wet paint weight, delivering broad-spectrum control against Pseudomonas aeruginosa (ATCC 15442) and Enterobacter aerogenes in the alkaline pH 7.5–9.0 range typical of carbonate-filled formulations, without generating formaldehyde-releasing moieties or volatile organic compounds (VOCs) that contribute to indoor air quality violations under ISO 16000-3:2011. The additive is introduced during the let-down phase of paint manufacturing, post-pigment grind on a high-speed disperser (tip speed 18–25 m/s), to avoid thermal degradation above 50°C and ensure uniform distribution at the final viscosity of 95–105 Krebs Units. The final products are 5 L, 10 L, and 15 L containers of tintable emulsion paints bearing the Blue Angel (RAL-UZ 102) and EU Ecolabel certifications, with preservative efficacy validated through a modified ISO 11930:2019 challenge test (28-day mixed inoculum, six inoculation cycles) showing a 4-log reduction within 48 hours. Corrosion of tinplate can bodies during long-term warehouse storage in tropical climates (40°C, 85% RH) is mitigated by the compound’s ability to passivate the tin-iron couple without the use of nitrite-based flash rust inhibitors, as confirmed by an internal tinplate immersion test based on ASTM B895-16. When Hydrogen Sulfide and Dissolved Copper Co-Exist in Sour Water Stripper BottomsIn oilfield produced water treatment facilities where ammonium bisulfide and dissolved copper from corroded brass valve components co-exist in a pH 6.8–8.2 range, the precipitation of copper sulfide (Ksp ≈ 6×10⁻³⁷) generates tenacious colloidal scales that blind tray-type stripper internals and plug downstream walnut shell filtration media within 72 hours of operation. The trisodium salt, with its strong thiolate ligation to Cu(I), shifts the equilibrium away from CuS nucleation by forming a stable, water-soluble complex ion, while simultaneously inhibiting hydrogen blistering of carbon steel through a monomolecular chemisorbed layer; this dual function is evaluated per NACE TM0284-2016 (hydrogen-induced cracking) and NACE SP0108-2008 (corrosion control for treatment plants) with target corrosion rates on AISI 1018 steel maintaining < 0.03 mm/y. The chemical is dosed continuously via positive displacement diaphragm pumps at a feed rate of 15–40 mg/L (as active base) into the produced water header upstream of the degasser, following a compatibility screening against scale inhibitors that must verify no formation of insoluble calcium-thiolate complexes at total dissolved calcium levels exceeding 2,000 mg/L. The downstream operational sequence involves flowing treated water through corrugated plate interceptors (CPI) and induced gas flotation (IGF) units before deep well disposal or reuse in hydraulic fracturing, with finished formulation delivered as a 30% active solution in tote tanks under UN 3264 corrosive liquid classification. Production operation logs from the Permian Basin indicate that switching from a conventional phosphonate-based program to a triazole-free thiolate corrosion inhibitor scheme reduced copper-induced FeS scaling frequency by 60% over a 180-day evaluation period when the trisodium salt residual was maintained at 25 ± 3 mg/L, measured by the Hach sulfide method adapted with masking agents. Recycled containerboard mills operating at neutral to alkaline pH (6.8–8.0) in 100% post-consumer OCC (old corrugated containers) furnish contend with rapid biofilm formation on stainless steel 316L chest surfaces and polypropylene forming fabrics, where slime-forming species such as Deinococcus geothermalis and Meiothermus silvanus exhibit resistance to oxidative biocides at chlorine dioxide residuals below 0.5 mg/L. Incorporation of 2,3-dihydro-5-mercapto-3-oxo-4-isothiazolecarboxylic acid trisodium salt at a dosage of 0.5–1.5 mg/L active into the short white-water loop (post-disk filter) reduces ATP bioluminescence readings to < 100 RLU within a 3-hour contact time without contributing to adsorbable organic halogen (AOX) formation, a critical requirement under the EU Best Available Techniques Reference Document (BREF) for Pulp and Paper (BAT 7). The bactericide is metered via a pulsation-free gear pump from a 200 L drum into the consistency-controlled white-water tank, where a targeted redox potential (ORP) range of 120–180 mV (Ag/AgCl reference) is maintained to optimize thiol stability and prevent premature oxidation to disulfide. The finished treated water is recycled directly to the wire pit and ultimately results in paperboard with recyclability certification (DIN EN 13430) and compliance to BfR Recommendation XXXVI for food contact, as the compound’s non-volatile, salt-form nature prevents migration into the dry board at detectable limits (< 1 µg/dm²) under the prescribed cold-water extraction (EN 645) test. Sulfur-Labile Passivation Films on Polyamide Membrane Feed SpacersReverse osmosis (RO) trains operating upstream of boiler feedwater demineralizers frequently employ copper-nickel interstage coolers to maintain a feed temperature below 35°C; however, trace copper dissolution (10–50 µg/L) catalyzes oxidative degradation of the polyamide thin-film composite layer when chlorine-neutralized water still carries transition metal ions. The trisodium salt, dosed at 2–5 mg/L into the micron cartridge filter inlet, forms a labile thiolate monolayer on stainless steel 316L spool surfaces and copper alloy heat exchange tubing, effectively reducing heterogenous catalytic sites responsible for peroxide radical generation. Membrane autopsy studies following 12-month exposure under cyclic concentration conditions (75% recovery, flux 20 LMH) demonstrated a 40% lower rate of salt passage increase when compared to systems treated only with a phosphonate antiscalant, as verified by standard cell testing per ASTM D4194-20 (standard test methods for operating characteristics of reverse osmosis and nanofiltration devices). The compliance framework draws on NSF/ANSI/CAN 61 for drinking water system components when the permeate is destined for food and beverage applications, and the reject stream’s copper content must meet the local sewer discharge limit of 0.5 mg/L Cu, a parameter controlled by the in-situ complexation equilibrium. The concentrate is prepared as a 25% aqueous solution buffered with potassium hydroxide, delivered in 55-gallon steel-reinforced polyethylene drums, and injected using an LMI Milton Roy solenoid-driven metering pump controlled by a 4-20 mA flow-paced signal. Finished potable water produced from brackish feed meets US EPA National Primary Drinking Water Regulations (NPDWR) for copper (1.3 mg/L action level) and shows no formation of disulfide by-products that could foul membrane spacers. |
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| Organism | 2,3-Dihydro-5-Mercapto-3-Oxo-4-Isothiazolecarboxylic Acid Trisodium Salt | MIT (50%) | BIT (20%) | CMIT/MIT (1.5%) | |
|---|---|---|---|---|---|
| P. aeruginosa | 75 | 200 | 350 | 25 | |
| M. immunogenum | 50 | 150 | >400 | 12 | |
| Fusarium solani | 40 | 300 | 100 | 80 |
| Parameter | Specification Limit | Method | Typical Value |
|---|---|---|---|
| Active content (as trisodium salt) | 49.0–51.0 % w/w | HPLC-UV, λ = 275 nm | 50.2 % |
| pH (as is, 25°C) | 10.5–12.0 | ISO 976:2013 | 11.3 |
| Density (20°C) | 1.28–1.32 g/mL | ISO 2811-1:2016 | 1.30 g/mL |
| Free mercaptan (as –SH) | ≥ 9.5 % w/w | Iodometric titration | 9.8 % |
| Iron (Fe) | ≤ 15 ppm | ICP-OES | 6 ppm |
| Clarity | Clear, pale yellow | Visual inspection | Pass |