|
HS Code |
107237 |
| Chemical Formula | C8H7NS2 |
| Molar Mass | 181.28 g/mol |
| Appearance | Yellow - orange solid |
| Odor | Characteristic sulfur - like odor |
| Melting Point | 117 - 119 °C |
| Solubility In Water | Insoluble |
| Solubility In Organic Solvents | Soluble in common organic solvents like ethanol, chloroform |
| Stability | Stable under normal conditions, but may decompose on heating or in contact with strong oxidizing agents |
As an accredited N-Methylbenzothiazole-2-Thione factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | 100g of N - Methylbenzothiazole - 2 - Thione packaged in a sealed, labeled container. |
| Shipping | N - Methylbenzothiazole - 2 - Thione is shipped in tightly sealed, corrosion - resistant containers. Transport follows strict chemical safety regulations, ensuring protection from environmental factors during transit. |
| Storage | N - Methylbenzothiazole - 2 - Thione should be stored in a cool, dry, and well - ventilated area. Keep it away from heat sources, flames, and oxidizing agents. Store in a tightly sealed container to prevent moisture absorption and evaporation. This helps maintain its chemical integrity and reduces the risk of reactivity with other substances. |
```Why Waterborne Architectural Coatings Require Broad-Spectrum Preservatives Beyond IsothiazolinonesStyrene-acrylic, pure acrylic, and vinyl acetate-ethylene (VAE) copolymer dispersions formulated with cellulosic thickeners, associative polyurethane rheology modifiers, and starch- or dextrin-based fillers routinely support proliferation of Pseudomonas aeruginosa, Enterobacter cloacae, and Aspergillus niger during sealed-container warehousing at ambient temperatures exceeding 25 °C. When methylisothiazolinone (MIT) or benzisothiazolinone (BIT) alone fails to suppress spore germination in high-pH, ammonia-neutralized systems, N-methylbenzothiazole‑2‑thione provides an electron-transport-chain inhibitor function that arrests fungal respiration at the cytochrome bc1 complex, complementing thiazolinone-based electrophilic attack on microbial thiol-containing enzymes. The active substance has been notified under EU Biocidal Products Regulation 528/2012 for product-type PT 6 (in-can preservation) and PT 7 (dry-film protection), with analytical verification performed via HPLC‑UV at 254 nm according to an internally validated method aligned with CEN/TR 16508. In-can challenge testing follows ASTM E2179‑18 with mixed bacterial/fungal inocula at 10⁷–10⁸ CFU/mL, while dry-film resistance is evaluated under ASTM D3273‑16 in an environmental chamber maintained at 32.5 ± 1 °C and 95 ± 3 % relative humidity over 28 days. The addition level ranges from 0.08 % to 0.30 % w/w on total formulation weight, adjusted upward when the recipe contains high proportions of water (> 45 %), coarse extenders hosting entrapped bioburden, or pH buffered above 9.0. During manufacturing, the biocide is introduced post‑pigment‑grind at the let‑down stage into a vessel equipped with a toothed disc disperser running at a peripheral speed of 15–18 m/s; batch temperature is maintained below 35 °C by jacket cooling, and the compound is stirred for 20–30 min to achieve homogeneous partitioning between the aqueous phase and the latex particle surface, while avoiding entrapment in micellar thickener networks that would reduce bioavailability. The finished preservative-treated formulations are compliant with GB 18582‑2020 indoor decorating and refurbishing coatings limits, EU Ecolabel criteria for indoor paints (Commission Decision 2014/312/EU), and REACH Annex XVII entry 72 restrictions on CMR substances. End-use articles include interior matt emulsion paints, waterborne wood varnishes, polyvinyl acetate (PVAc) wood adhesives, and cementitious waterproofing slurries where fungal defacement leads to premature re-coating intervals.
Leather Wet-Blue Preservation and Finished Article FungistasisSemichrome and vegetable-tanned wet-blue stock stored at 60–70 % moisture content under tropical warehouse conditions (ambient 28–35 °C, RH > 85 %) without effective fungicidal treatment develops Penicillium chrysogenum and Trichoderma viride colonies within 72–96 h, leading to irreversible grain damage and tensile strength loss exceeding 15 % in the final crust. N‑methylbenzothiazole‑2‑thione, as a non‑phenolic heterocyclic biocide, exhibits a biphasic uptake mechanism into the collagen triple‑helix interstices, with a partition coefficient (log Kow) of approximately 2.1 that ensures sufficient fiber substantivity without over‑accumulation in natural fat liquors. Application is governed by ZDHC MRSL 2.0 conformance and REACH Annex XVII restriction protocols on skin‑sensitizing substances; migration into finished leather is quantified by extraction with artificial perspiration solution per ISO 17226‑2:2018 and detected via LC‑MS/MS with a reporting limit of 0.5 mg/kg. Typical addition rates range from 0.12 % to 0.25 % on shaved wet-blue weight, pre‑dispersed in a non‑ionic emulsifier package (HLB 12–14) before being introduced into the retanning or fatliquoring drum. The float ratio is maintained at 50–80 %, temperature at 30–40 °C, and drumming time between 45 and 60 min; pH is adjusted with sodium formate or sodium bicarbonate to a window of 3.8–4.5 to maximize protonated‑state binding without causing chrome‑soap‑induced grain haze. Post‑drum, sammying and setting pressures above 40 bar should be avoided until the biocide has fully equilibrated, typically after 4–6 h of muleing. The preserved stock is subsequently finished with polyurethane or acrylic topcoats that do not interfere with the active migration barrier. Finished articles include automotive upholstery leather requiring heat‑aging resistance 7 days at 120 °C without visible discoloration, furniture split leather, and safety footwear upper leather meeting EN ISO 20345:2021 flex endurance. Papermaking white water systems operating under neutral to slightly alkaline conditions (pH 7.2–8.5) with closed‑loop water recycling beyond 95 % accumulate dissolved organic carbon loads exceeding 2000 mg/L and cultivate biofilm‑forming bacteria such as Burkholderia cepacia, Deinococcus geothermalis, and filamentous fungi including Chaetomium globosum that degrade fiber‑fiber bonding, produce volatile fatty acid catabolites causing off‑odor in finished board, and plug forming fabrics with extracellular polymeric substances. An N‑methylbenzothiazole‑2‑thione‑based slimicide conforms to FDA 21 CFR 176.170 when used at levels not exceeding 0.04 % by weight of the dry fiber, permitting direct food‑contact paper and paperboard applications, and is registered under FIFRA with 40 CFR 152 labeling requirements for industrial preservative use. The dosage is metered at 100–400 g per metric ton of bone‑dry pulp via a diaphragm dosing pump into the machine chest or white‑water silo, with a static mixer located 12–15 s of residence time upstream of any cationic retention aid injection point to prevent charge‑neutralization‑driven precipitation of the active—especially critical when single‑polymer polyacrylamide (C‑PAM) programs carrying a charge density above 3.5 meq/g are employed. System efficacy is monitored by ATP bioluminescence swab testing of suction couch roll surfaces, with a target of < 200 RLU, and by daily plate counts on TSA/SDA agar with 48 h incubation. The manufacturing process integrates the slimicide at the wet end; the treated stock is then refined to 28–35 °SR freeness, formed on a gap former at 850–1200 m/min, pressed to 48–52 % solids, and dried in a multi‑cylinder section where the peak web temperature of 105 °C does not cause thermal decomposition of the biocide (onset of degradation observed at 198 °C by TGA). Terminal products comprise liquid‑packaging board compliant with EN 647:2022, gypsum liner, and grease‑resistant folding carton stock. When EPDM Compounding Requires a Non‑Nitrosamine‑Generating Sulfur DonorEthylene‑propylene‑diene monomer (EPDM) compounds destined for automotive coolant hoses, building seals, and potable water gaskets are frequently formulated with sulfur‑donor curatives to generate mono‑ and disulfidic crosslinks that confer superior heat‑aging resistance and compression set values below 15 % after 70 h at 150 °C (tested per ISO 815‑1:2020). Conventional carbamate‑ and thiuram‑based donors release secondary amines that can form N‑nitrosamines under acidic condensation, triggering regulatory action under TRGS 552 and GB 2760 restrictions for rubber contacting dry food. N‑methylbenzothiazole‑2‑thione, a thione‑tautomer‑dominant sulfur carrier with an effective sulfur content of 29–31 %, decomposes during the vulcanization plateau to liberate active sulfur radicals without generating secondary amine by‑products. The compound is added at 1.8–3.2 phr in conjunction with primary accelerators such as MBTS (dibenzothiazyl disulfide) at 0.8–1.2 phr or ZDBC (zinc dibutyldithiocarbamate) at 0.3–0.6 phr to modulate scorch safety. Processing is executed on an intermeshing tangential rotor internal mixer (Banbury F‑series, 1.6 L chamber) with a fill factor of 0.75, ram pressure 4.5 bar, and rotor speed 55 rpm; the masterbatch drop temperature is capped at 125 °C to prevent premature sulfur release. After dumping, the compound is sheeted on a two‑roll mill with a friction ratio of 1:1.15 at a nip gap of 3 mm and rolled into a continuous strip for cold‑feed extrusion through a 90 mm pin‑barrel extruder with an L/D of 16:1 at a screw temperature of 40 °C and head temperature of 80 °C. Vulcanization is monitored with a moving‑die rheometer (MDR) per ASTM D5289‑19a at 170 °C, 1° arc, ensuring T90 is reached in the mold without exceeding a pressure drop that would cause porosity in profiles thicker than 8 mm. Finished goods include EPDM radiator hoses meeting SAE J20 Class D specifications, low‑permeability O‑rings for R‑134a refrigerant systems, and architectural glazing gaskets complying with EN 12365‑1:2003 recovery after compression.
Water‑miscible metalworking fluids (MWFs) formulated as semi‑synthetic or full‑synthetic dilutable concentrates encounter severe microbial challenges once diluted to 3–8 % in service water at sump temperatures between 30 °C and 40 °C and pH maintained between 8.8 and 9.5. Mycobacterium immunogenum, Pseudomonas oleovorans, and sulfate‑reducing bacteria (SRB) generate slime rafts that block central system filters (porosity 20–50 µm), produce hydrogen sulfide‑induced corrosion on aluminum‑alloy engine components, and increase the total acid number (TAN) beyond 5 mg KOH/g, rapidly destabilizing the emulsion. An N‑methylbenzothiazole‑2‑thione‑based preservative registered under EU BPR product‑type PT 13 and compliant with ASTM E2880‑20 bioresistance testing delivers broad‑spectrum control when incorporated into the concentrate at 0.8 %–1.5 % w/w, yielding a working‑fluid active concentration of 100–300 mg/L at the point of use. The manufacturing sequence adds the biocide as the final component into the blending vessel after all emulsifiers, alkanolamine‑borate corrosion inhibitors, and extreme‑pressure sulfurized fat additives have been homogenized; the batch is circulated through a high‑shear rotor‑stator assembly running at 3000 rpm for 45 min at a temperature not exceeding 45 °C, and alkalinity is maintained at a reserve alkalinity value of 15–25 mL of 0.1 N HCl to pH 4.0. On the shop floor, the concentrate is proportioned into service water through a venturi mixer, and sump bioburden is monitored weekly using dip‑slides incubated for 48 h at 30 °C; a total viable count (TVC) exceeding 10⁵ CFU/mL triggers a shock dose of the concentrate directly into the return line. Operational boundaries require that the fluid pH never drops below 8.3, as the thione tautomer hydrolyzes at a half‑life of 18 h at pH 7.0 and 35 °C. End‑use fluids meeting ISO 6743‑7 classification include multi‑purpose semi‑synthetic coolants for ferrous and non‑ferrous machining, and synthetic grinding fluids for tungsten‑carbide tool production where rinse‑off protection is essential for inter‑stage storage. Polyester‑cotton blended fabric engineered for outdoor tensile structures and truck tarpaulins is typically finished with a durable antimicrobial agent through a pad–dry–cure sequence that demands a biocide possessing moderate water solubility (approximately 200–500 mg/L), adequate sublimation resistance at curing temperatures between 140 °C and 160 °C, and minimal interference with fluorocarbon‑based water‑repellent finishes applied in the same bath. N‑methylbenzothiazole‑2‑thione applied as an aqueous dispersion (mean particle size 2–5 µm, stabilized with an anionic naphthalene sulfonate condensate at 3 % on weight of active) is compatible with weakly acidic to neutral pad liquors and does not chelate with the aluminum/zirconium salts used in the subsequent cross‑linking of fluorotelomer polymers. The treatment is governed by OEKO‑TEX Standard 100 Annex 4 and ZDHC MRSL 2.0, with absorption determined by the limit of quantification of 0.5 mg/kg for benzothiazole residues in artificial sweat extract per ISO 14362‑3:2022. Addition rate is set at 1.5 %–3.0 % on weight of fabric (owf) in the pad bath, which is applied via a two‑dip two‑nip padding mangle with a squeeze‑roll pressure of 2.5 bar to achieve a wet pick‑up of 68–72 %, resulting in a dry add‑on of 1.0 %–2.0 % owf. The fabric is then dried in a tensionless belt dryer with zone‑1 temperature 110 °C for 90 s and cured in a stenter frame at 150 °C for 120 s; the dwell time in the curing zone is verified by a traveling thermocouple probe to avoid front‑to‑back shade variation and over‑drying that would cause yellowing when peroxide‑bleached cotton is present. Efficacy is validated using AATCC TM30‑2017 (Antifungal Activity, Assessment on Textile Materials) against Aspergillus niger and Chaetomium globosum with a target rating of 2 or better (no sporulation) after 10 cycles of simulated weathering per AATCC TM186‑2022. Final end‑articles include PVC‑coated polyester truck side‑curtains, acrylic‑canvas awnings, and geotextile reinforcement fabrics embedded in retaining wall systems subject to prolonged contact with nutrient‑rich soil leachate. Given Chlorine Dosing Limits in Alkaline Cooling Water, Alternative Electron Transport InhibitorsOpen recirculating cooling systems operating with make‑up water alkalinity above 200 mg/L as CaCO₃ and pH held in the range 8.5–9.2 by organic phosphonate and polymer dispersant programs experience a rapid decline in hypochlorite‑based biocide efficiency because the equilibrium shifts to the less‑biocidal hypochlorite ion (pKa of HOCl = 7.54 at 25 °C), while excessive chlorine dosing accelerates trihalomethane formation and breaks down tolyltriazole‑based copper corrosion inhibitors. N‑methylbenzothiazole‑2‑thione, acting as a respiratory chain inhibitor at Complex III, is applied as a non‑oxidizing shock biocide under EU BPR product‑type PT 11 with a notified maximum in‑service concentration of 50 mg/L, and is compatible with azole‑based yellow metal inhibitors at levels up to 8 mg/L active. The dosing protocol injects a neat liquid formulation (typical active content 15 % solubilized in glycol‑ether‑water carrier with a flash point above 100 °C) directly into the cooling tower basin sump at a concentration of 30–50 mg/L product, equivalent to 4.5–7.5 mg/L active, on a weekly cycle with alternating non‑oxidizing chemistries such as glutaraldehyde or DBNPA to prevent resistant sessile populations. The sump must be equipped with a chemical dosing pump interlocked with the main circulation pump and a conductivity controller; injection is performed over a 30–60 min period while the system is at peak recirculation, and the pH is temporarily lowered to 8.3 using sulfuric acid dosing 30 min prior to introduction to suppress instantaneous hydrolysis. Monitoring of the active residue is accomplished by cyclic voltammetry with a glassy carbon electrode, calibrated against a standard addition of the thione in synthetic cooling water matrix, tracking a peak current at +1.12 V vs. Ag/AgCl. System compliance with GB/T 23849‑2009 test methods for bacterial sludge inhibition and with ASTM E2275‑19 (Standard Practice for Evaluating Water‑Miscible Metalworking Fluids and General Service Fluids, adapted for cooling systems) is documented quarterly. Treated process water serves ethylene cracker quench‑water loops, ammonia refrigeration condenser circuits, and power‑plant auxiliary cooling loops where biofilm‑induced under‑deposit corrosion on carbon steel (often exceeding 0.5 mm/year in untreated condition) must be suppressed without exceeding the total chlorides limit of 200 mg/L set by the steam generator vendor. ``` |
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| Property | Value | Test Method |
|---|---|---|
| Appearance | Pale yellow crystalline powder | Visual; AFERA 4012 P3 |
| Purity (HPLC) | ≥ 97.5 % | In-house HPLC, external standard |
| Melting range | 66–70 °C | ASTM E794 (DSC, 10 K/min) |
| Moisture | ≤ 0.5 % | ASTM E203 (Karl Fischer) |
| Ash (sulfated) | ≤ 0.1 % | ASTM D5667 |
| Solubility in acetone (25 °C) | > 50 g/L | Gravimetric |
| Bulk density (tapped) | 0.50–0.65 g/cm³ | ASTM D1895 Method B |
| Accelerator Property | NMBT | MBT | ZMBT | MBTS |
|---|---|---|---|---|
| Abbreviation | NMBT | MBT | ZMBT | MBTS |
| Scorch safety index (MBT = 1) | 2.5–3.0 | 1.0 | 0.8–1.2 | 1.5–2.0 |
| Activation temperature (°C) | 130–140 | 100–115 | 90–105 | 110–125 |
| Bloom tendency | Low | High | Medium | Medium |
| Suitable elastomers | NR, SBR, BR, EPDM, IIR | NR, SBR, BR, IR | NR, SBR, BR, EPDM | NR, SBR, BR, IIR, EPDM |
| Typical dosage (phr) as secondary | 0.2–0.7 | 0.2–0.5 | 0.5–1.5 | 0.5–1.2 |
| Zinc content | None | None | Yes (∼16 % Zn) | None |