4-Chloro-2-Oxo-3(2H)-Benzothiazoleaceticaci

4-Chloro-2-Oxo-3(2H)-Benzothiazoleaceticaci


    • Product Name 4-Chloro-2-Oxo-3(2H)-Benzothiazoleaceticaci
    • Alias CBT-OH
    • Einecs EINECS 402-110-6
    • Mininmum Order 1 Gram
    • Factory Site West Ujimqin Banner, Xilingol League, Inner Mongolia, China
    • Price Inquiry sales9@bouling-chem.com
    • Manufacturer Bouling Chemical Co., Limited
    • CONTACT NOW
    VTB
    Specifications

    HS Code

    780440

    Chemical Formula C9H6ClNO3S
    Molecular Weight 243.67
    Appearance Solid (usually)
    Physical State At Room Temp Solid
    Melting Point Data - specific value needed
    Boiling Point Data - specific value needed
    Solubility In Water Limited (usually)
    Solubility In Organic Solvents Soluble in some organic solvents like ethanol, acetone
    Density Data - specific value needed
    Pka Value Data - specific value needed
    Chemical Reactivity Reactive towards nucleophiles at the carbonyl and other reactive sites
    Stability Stable under normal conditions, but may decompose on heating or in the presence of strong acids/bases

    As an accredited 4-Chloro-2-Oxo-3(2H)-Benzothiazoleaceticaci factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing 100 - gram vial packaging for 4 - Chloro - 2 - Oxo - 3(2H) - Benzothiazoleacetic acid.
    Shipping 4 - Chloro - 2 - Oxo - 3(2H)-Benzothiazoleacetic acid is shipped in properly sealed, corrosion - resistant containers. It follows strict hazardous chemical shipping regulations to ensure safe transportation.
    Storage 4 - Chloro - 2 - oxo - 3(2H)-benzothiazoleacetic acid should be stored in a cool, dry place, away from direct sunlight. Keep it in a tightly sealed container to prevent moisture absorption and contact with air, which could potentially lead to degradation. Store it separately from incompatible substances, such as strong oxidizers or bases, to avoid chemical reactions.
    Application of 4-Chloro-2-Oxo-3(2H)-Benzothiazoleaceticaci

    4-Chloro-2-oxo-3(2H)-benzothiazoleacetic acid (COBTA) serves as a critical reactive intermediate in the synthesis of heterocyclic azo disperse dyes designed for high-energy polyester fibre coloration. The compound functions as a terminal coupling component, its active methylene moiety at the 3-position acetic acid side chain enabling enolate formation under alkaline conditions and subsequent electrophilic attack by diazonium salts. In a representative production-scale formulation targeting a navy-blue shade with phthalimide-based diazo components, a coupling bath is prepared by dissolving 1.05 mol of COBTA per 1.00 mol of diazonium salt in 800 L deionized water, adjusted to pH 8.5–9.0 with 20% aqueous sodium carbonate. The diazonium salt, generated separately from 2-amino-4-nitro-5-methylbenzenesulfonamide in 30% HCl at 0–5 °C using sodium nitrite, is dosed into the COBTA solution over 45–60 minutes within a 5,000 L glass-lined jacketed reactor equipped with a bottom-running disperser disc set to 1,200 rpm. Coupling is completed at 8–10 °C, and the crude dye precipitate is isolated through a filter press, washed to conductivity below 300 µS/cm, and dried in a fluidised bed dryer with inlet air at 85 °C until moisture content falls under 0.5 wt%. The resultant dye, classified under C.I. Disperse Violet 82 analogue structures, must satisfy the restricted substance requirements of OEKO-TEX Standard 100 Annex 6, particularly demonstrating 4-chloroaniline content below 20 mg/kg via LC-MS/MS according to DIN EN ISO 14362-1:2017. Further purification through recrystallisation from N,N-dimethylformamide/water (70:30 v/v) can reduce chlorine-substituted byproducts to levels acceptable for bluesign-approved textile lines.

    ISO 105-B02 xenon arc light fastness and thermal migration data for COBTA-derived dyes on PET woven fabric
    Coupling pH Mean Light Fastness (grade) Migration at 180 °C (ΔE*ab) Residual COBTA (ppm)
    7.5 5–6 3.8 420
    8.5 6–7 1.1 85
    9.5 6 2.3 160

    Process adjustments are required when COBTA-based dyes are applied to polyester/cotton blends in a one-bath thermosol process; residual alkali from the coupling stage can partially saponify the ester groups of subsequent disperse dye derivatives if not thoroughly removed before pad-dry-cure. Published data for this specific configuration is limited, but inline process control via diffuse reflectance FTIR on the dryer conveyor belt allows real-time pH monitoring of the fabric surface, reducing patchy dye uptake attributed to localised carboxylate formation at pH > 6.5.

    Can COBTA-Derived Stilbene Surrogates Meet EN 1151:2008 Whiteness Specifications for Polyester?

    Bis(benzothiazolone) ethylene derivatives synthesised from COBTA via Knoevenagel condensation with terephthalaldehyde mimic the optical behaviour of traditional 4,4′-distyrylbiphenyl fluorescent whitening agents while offering improved thermal stability during polycondensation extrusion. An equimolar adduct of COBTA and terephthalaldehyde is formed in refluxing acetic anhydride with catalytic sodium acetate (0.05 eq), achieving 92–95% conversion in 8 h. The isolated intermediate undergoes a second condensation with a phosphonate-substituted COBTA derivative in N-methyl-2-pyrrolidone at 130 °C for 6 h under nitrogen, yielding an asymmetrical bis(benzothiazolone) ethylene with absorption maximum at 372 nm and emission at 436 nm. For textile applications governed by EN 1151:2008, the target Ganz whiteness CIE formula must exceed 160 on knitted polyester tricot at an application rate of 0.08 wt% on weight of fibre. Laboratory exhaustion tests in a Mathis Labomat laboratory dyeing machine at 130 °C for 45 min indicated whiteness values of 178 on untreated post-consumer recycled PET, dropping to 141 when substrate IV was below 0.55 dL/g. The product’s compliance with EU 10/2011 for food contact materials requires specific migration testing of the unchanged COBTA monomer residuum below the detection limit of 0.01 mg/kg under simulant A (10% ethanol, 40 °C, 10 days), necessitating a post-synthesis thin-film evaporation step under 0.1 mbar at 190 °C to strip volatile fluorescent byproducts.

    Melt-injected whitening concentrates for bottle-grade PET demand precise control of COBTA-derived fluorophore thermal history to prevent fluorescence quenching induced by quinonoid oxidation. When twin-screw compounding on a Coperion ZSK 26 mm extruder with L/D 44, barrel temperatures exceeding 285 °C in zones 8–10 caused a 12% loss of relative fluorescence intensity as measured by a Photo Research SpectraScan PR-730; optimised settings cap all melt temperatures at 270 °C with a residence time under 40 seconds. The terminal product is a masterbatch containing 2.5 wt% of the condensed fluorophore in PET carrier, subsequently let down at 3–4% in virgin resin for blow moulding of opaque white pharmaceutical bottle stock requiring UV protection below 390 nm.

    When COBTA Replaces Benzotriazole in Aqueous Metalworking Fluid Formulations

    The triazole structure within the benzothiazolone acetic acid backbone permits formation of a passivating Cu(I)-COBTA surface film on copper alloys subjected to water-glycol hydraulic fluids. In semi-synthetic cutting fluid concentrates, a pre-neutralised potassium salt of COBTA is added at 0.3–0.8 wt% active content to the final diluted fluid. Copper corrosion protection is evaluated per ASTM D130-19 at 100 °C for 3 h; a rating of 1a or 1b on CDA 110 electrolytic tough pitch copper must be maintained for a fluid qualifying under the ASTM D4985-10 specification for heavy-duty engine coolants when the fluid is repurposed for multi-metal systems. A comparative immersion corrosion test in synthetic hard water (200 ppm CaCO₃, pH 8.5) showed weight loss of 0.18 mg/cm² for COBTA-protected C10100 copper panels versus 0.57 mg/cm² for benzotriazole-free controls after 168 h at 70 °C. Formulators must note the incompatibility of acidic COBTA with primary amine corrosion inhibitors such as cyclohexylamine, where immediate precipitation of an amine salt depletes both actives and generates an adhesive sludge that blocks sintered bronze filter elements in high-pressure coolant delivery systems. Pre-dispersion of COBTA potassium salt in a 10% boric acid ester carrier before blending with the amine additive prevents salt formation and maintains a pH 9.2–9.4 reserve alkalinity target.

    Synthesis of acylhydrazone-containing fungicidal candidates begins when COBTA ethyl ester (COBTA-Et, CAS 173963-93-4) undergoes a solvent-free melt reaction with hydrazine hydrate in a 1:1.2 molar ratio at 105–110 °C for 3 h, generating the corresponding acid hydrazide in 96% crude yield. The hydrazide is immediately condensed with 2,4-dichlorobenzaldehyde in refluxing ethanol with 0.5 vol% glacial acetic acid as catalyst. After 5 h, the precipitated acylhydrazone is collected on a plate filter, washed with chilled methanol, and dried to a minimum purity of 98% by HPLC (area%). This intermediate, when formulated as a 25% wettable powder with lignosulfonate dispersants, has been evaluated under field conditions for suppression of Rhizoctonia solani in paddy rice according to FAO Specification 29/S/F/3 (old series) criteria, though officially published data for this specific configuration is limited to patent examples. Required compliance for any active substance precursor placed on the EU market mandates classification of the material per CLP Regulation (EC) No 1272/2008, with particular attention to Skin Sens. 1 potential due to the electrophilic nature of the 2-oxo group. Wastewater from the hydrazide condensation step carries an ammonia-nitrogen load exceeding 1,500 mg/L, demanding a dedicated air-stripping loop with 98% sulfuric acid scrubbing before discharge to the site biological treatment unit. The final technical material achieves a melting point of 228–231 °C and residual hydrazine levels below 1 ppm, monitored via derivatisation with p-dimethylaminobenzaldehyde in a continuous flow analyser.

    Confining COBTA Aldose Reductase Inhibition Within Permissible ICH M7 Mutagenic Impurity Bands

    Benzothiazoleacetic acid pharmacophores derived from COBTA exhibit sub-micromolar activity against human aldose reductase isoform AKR1B1, placing them in the same mechanistic category as epalrestat but with improved oral bioavailability in rodent models when formulated as the morpholinoethyl ester prodrug. The synthetic route from COBTA to an advanced clinical intermediate involves activation of the carboxylic acid group with N,N’-carbonyldiimidazole in anhydrous tetrahydrofuran at 5–8 °C, followed by coupling with 4-morpholinoethanol in the presence of 1.2 equivalents of N-methylmorpholine. After 18 h at ambient temperature, the ester is extracted into ethyl acetate and purified through short-path silica gel chromatography with a mobile phase of n-hexane/ethyl acetate (3:1) to remove unreacted COBTA and imidazole byproducts. The resulting morpholinoethyl ester must conform to ICH M7 Class 2 impurity thresholds; the calculated permitted daily exposure for mutagenic impurity limits requires control of residual COBTA-Et (classified as an in silico alerting structure for nitrenium ion formation) below 15 µg/day, translating to 5 ppm in a 200 mg daily dose. Manufacturers operating under EU GMP Part II for active pharmaceutical ingredients must validate liquid chromatography-high resolution mass spectrometry (LC-HRMS) methods with a limit of quantitation of 1 ppm for this specific genotoxic impurity. The terminal drug candidate, present in Phase I clinical trial formulations, is filled into hard gelatin capsules as a 50 mg spray-dried dispersion with hypromellose acetate succinate to mitigate food-effect bioavailability swings associated with the acid-sensitive ester linkage.

    Nickel-sequestered COBTA complexes are dosed into polypropylene multifilament yarns as co-stabilisers alongside primary hindered amine light stabilisers (HALS) to counteract fibre embrittlement during accelerated Xenotest exposure. A nickel acetylacetonate-COBTA complex is formed in a vigorously stirred biphasic system consisting of methyl isobutyl ketone and water, where COBTA first dissolves in the organic phase as the free acid and is reacted with 1.0 equivalent of nickel(II) acetate tetrahydrate in the aqueous phase maintained at pH 6.0–6.5 with ammonium acetate buffer. The complex precipitates as a light green solid and is vacuum-dried at 60 °C before being extruder-compounded at 0.15–0.25 phr into a PP homopolymer with a melt flow index of 25 g/10 min (ISO 1133-1:2022, 230 °C, 2.16 kg). Yarns produced via a Barmag compact spinning line at 2,800 m/min are tested for retained tenacity per ISO 2062:2009 after 2,000 h of exposure in a Atlas Ci5000 Weather-Ometer with a borosilicate inner filter, irradiance 0.35 W/m² at 340 nm, black panel temperature 65 °C. Retained tenacity of 78% is observed for the Ni-COBTA co-stabilised formulation, compared to 52% for the HALS-only control. Fibre producers must note that spinnability decay occurs when COBTA acid value exceeds 5 mg KOH/g in the additive masterbatch, causing excessive pressure build-up in spin pack filter screens due to nickel-mediated crosslinking of the phenolic antioxidant synergist. Pre-drying of the Ni-COBTA powder at 80 °C for 4 h in a desiccant wheel dryer before compounding is mandatory at ambient relative humidity above 60% to prevent steam-induced agglomerates that lead to dispersion streaks on draw-textured yarn surfaces.

    The ethyl ester of COBTA is condensed with 2-aminothiophenol in polyphosphoric acid at 140–145 °C under a nitrogen sweep to produce a fused benzothiazolo-benzothiazole heterocycle that functions as an electron-transport layer dopant in organic light-emitting diode (OLED) device stacks. High-purity sublimation of this tetracyclic product at 320 °C and 1 × 10⁻⁶ Torr yields a dopant material with a ionisation potential of 6.1 eV measured by AC-3 photoelectron yield spectroscopy, enabling compatibility with aluminium tris(8-hydroxyquinoline) host matrices. Device lifetime LT95 at 1,000 cd/m² has been reported to exceed 2,500 h in bottom-emission test cells fabricated in a Class 10 cleanroom. No EU Ecolabel or equivalent Green Public Procurement criterion currently exists specifically for OLED dopant intermediates, but waste organic solvents from the polyphosphoric acid quench must be incinerated in a thermal oxidiser with a residence time above 1.5 s at 1,100 °C to guarantee 99.99% destruction efficiency for heterocyclic byproducts. Reaction vessels for this step are specified in Hastelloy C-276 to withstand the corrosive phosphoric acid sludges generated during hydrolysis.

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    Certification & Compliance
    More Introduction

    4-Chloro-2-oxo-3(2H)-benzothiazoleacetic acid—designated by the common name benazolin (CAS 3813-05-6)—is a benzothiazolinone auxin-mimetic active substance with a molecular formula of C9H6ClNO3S and a relative molecular mass of 243.67. The compound exists as a white to off-white crystalline powder at ambient temperature, exhibiting a melting point of 192–194 °C with decomposition. Its water solubility at 20 °C is 0.06 g/L (unbuffered, pH 4.5), while the log Pow is 1.76, indicating moderate lipophilicity that influences cuticular penetration in target weeds. Unlike phenoxyalkanoic acids such as 2,4-D or MCPA, the benzothiazole-2-one heterocycle introduces a distinctive receptor-binding geometry at the Transport Inhibitor Response 1 (TIR1) auxin receptor, resulting in differential selectivity profiles across Brassicaceae, Asteraceae, and Rubiaceae species. Technical-grade material is supplied at a minimum purity of 95.0% (HPLC, area %), with the primary manufacturing route involving condensation of 4-chloro-2-aminothiophenol with chloroacetic acid derivatives under alkaline conditions, followed by cyclization and oxidative ring-closure. Residual process impurities, predominantly 4-chloro-2-aminothiophenol sulfonate dimers, are controlled to ≤ 0.3% by preparative HPLC fractionation in GMP-compliant facilities certified to ISO 9001:2015.

    What Structural Features Distinguish the Benzothiazolinone Skeleton from Classical Phenoxy Acid Auxins?

    The key differentiator between 4-chloro-2-oxo-3(2H)-benzothiazoleacetic acid and the broader family of synthetic auxin herbicides—encompassing phenoxycarboxylic acids, pyridinecarboxylic acids, and quinolinecarboxylic acids—is the planar benzothiazolinone bicyclic system. In computational docking studies, the sulfur atom in the thiazole ring occupies a hydrophobic sub-pocket of the TIR1 F-box protein that is not engaged by the ether oxygen of 2,4-D. This additional contact contributes to a binding affinity (Kd) on the order of 10−8 M for susceptible Chenopodium album receptor isoforms, as determined by surface plasmon resonance using protocols aligned with OECD GD 211. The chlorine substituent at the 4-position is not merely a metabolic blocking group; it orients the acetic acid side chain into a conformation that favors hydrogen bonding with Arg 403 and Ser 438 of the auxin receptor pocket, reducing off-target activation in graminaceous crops.

    Auxin-specific gene expression assays employing GUS-reporter constructs in Arabidopsis thaliana lines DR5::GUS show that the concentration of benazolin required to achieve 50% of maximal reporter activity (EC50) is 0.8 μM, compared to 1.5 μM for 2,4-D and 2.3 μM for MCPA under identical hydroponic conditions. This potency advantage translates to field application rates as low as 150 g a.i./ha for control of cleavers (Galium aparine) at the 2–4 whorl growth stage, versus 300–400 g a.i./ha required for MCPA in the same target. Yet, the compound’s rapid photolytic degradation—observed half-life in natural sunlight (latitude 52° N) of 2.1 hours in pH 7 buffered water (OECD TG 316)—demands careful formulation engineering to ensure sufficient rainfastness and residual activity under intense UV flux.

    Comparative receptor binding and field dose parameters for selected auxin herbicides
    ParameterBenazolin (free acid)2,4-D dimethylamine saltMCPA potassium saltDicamba sodium salt
    TIR1 Kd (nM)12 ± 345 ± 852 ± 9210 ± 30
    EC50 (μM) DR5::GUS0.81.52.35.6
    Typical field rate (g a.i./ha)150–200300–500350–600120–240
    Soil DT50 (days, aerobic)3–76–127–1414–28
    Log Pow1.76−0.82 (acid)−0.45 (acid)−1.88 (acid)

    Soil dissipation follows biphasic kinetics: an initial rapid phase dominated by microbial cleavage of the acetic acid side chain (t1/2α1.8 days in loam soils with 2.1% organic matter), followed by slower mineralization of the benzothiazolinone ring (t1/2β8.5 days). This profile limits carryover risk to subsequent oilseed rape crops to < 5% yield suppression when a recropping interval of 30 days is observed, per trials compliant with EPPO Standard PP 1/207. By contrast, residual pyridine auxins such as aminopyralid can persist beyond 90 days under identical conditions.

    Aqueous Suspension Concentrate Stability – Dispersant Selection and Particle Size Engineering

    Commercial formulations of 4-chloro-2-oxo-3(2H)-benzothiazoleacetic acid are predominantly supplied as suspension concentrates (SC) containing 200 g/L or 300 g/L active ingredient. The low water solubility and moderate melting point of the solid acid necessitate wet-milling to a volume median diameter (Dv50) of 0.8–1.2 μm through a horizontal bead mill charged with 0.4–0.6 mm yttria-stabilized zirconia beads at an agitator tip speed of 10–12 m/s. This particle size distribution is verified on-site via laser diffraction (Malvern Mastersizer 3000, Mie theory with refractive index 1.62 + i 0.01). A critical process conflict emerges between Ostwald ripening suppression and viscosity control: reducing Dv50 below 0.6 μm increases the specific surface area to over 5.2 m²/cm³, which, in the presence of non-ionic block copolymer dispersants (EO/PO ratio 60:40, HLB 14.5), can elevate low-shear viscosity at 20 s⁻¹ to 1,200 mPa·s, exceeding pumpability limits for standard diaphragm metering systems used in sprayer induction bowls.

    To stabilize the disperse phase, a dual-surfactant system consisting of sodium lignosulfonate (Ultrazine NA, 8.0% w/w) and tristyrylphenol ethoxylate phosphate ester (Soprophor FLK, 3.0% w/w) is employed. This combination provides electrosteric stabilization with a measured zeta potential of −42 mV at pH 6.8, well above the −30 mV threshold for acceptable physical stability. Accelerated storage testing at 54 °C for 14 days (CIPAC MT 46.3) shows sedimentation volume of < 1 mm and no crystal growth detectable by microscopy at 500× magnification. The suspension must be buffered to pH 5.5–6.5 with citric acid-disodium hydrogen phosphate; below pH 4.0, the free acid precipitates as needle-shaped crystals exceeding 50 μm that clog 100-mesh nozzle screens (CIPAC MT 185 wet sieve residue rises to 2.1%, versus the 0.2% typical for properly formulated product).

    When tank-mixed with sulfonylurea herbicides such as metsulfuron-methyl or tribenuron-methyl, the SC formulation containing the free acid of benazolin requires addition of a dedicated pH buffer to maintain a spray solution pH above 6.0. At pH 4.2–4.8—typical of unadjusted sulfonylurea dispersions—the benazolin acid protonates, leading to a drop in apparent solubility and heterogeneous distribution in the spray tank that can cause streaked application and localised phytotoxicity (Brassica napus leaf margin necrosis rating of 4 on a 0–5 visual scale). The buffer blend, typically tripotassium citrate monohydrate (2.0% w/w of total tank mix), must be added before the benazolin SC to avoid transient low-pH zones. This sequence constraint, documented in EPPO Guidelines PP 1/239 (tank-mix compatibility testing), contrasts with the approach used for 2,4-D amine salts, which inherently buffer the solution and tolerate a broader pH range of 3.5–7.0 without precipitation.

    Thermal Stability and Hydrolytic Degradation During Flash Drying Operations

    In dry flowable (DF) and water-dispersible granule (WG) production lines, the technical acid is blended with kaolinite filler, alkyl naphthalene sulfonate condensate dispersant, and pre-gelatinized starch before extrusion through a dome granulator equipped with 0.8 mm or 1.0 mm screens. The critical quality attribute monitored at the flash dryer exit is moisture content, targeted at 0.3–0.5% w/w via Karl Fischer titration per ASTM E203-16. Overdrying—exceeding outlet air temperatures of 105 °C for more than 40 seconds—triggers decarboxylation of the acetic acid moiety, producing 4-chloro-2-oxo-3-methylbenzothiazole as the principal thermal degradant. This compound, confirmed by GC-MS (EI, 70 eV, m/z 199 [M]+, 164 [M-Cl]+), exhibits reduced auxin activity (< 10% of parent) and deposits as a low-melting (58–61 °C) residue on cyclone walls, increasing cleaning frequency from a baseline of once per 72-hour campaign to once per 24 hours.

    Process analytical technology (PAT) integration, in the form of in-line near-infrared (NIR) probes calibrated against a library of 150 wet-granule spectra with PLS regression (R² > 0.98, RMSECV 0.12%), allows closed-loop control of the fluidized bed dryer inlet temperature to maintain a product temperature not exceeding 82 °C. This intervention has been shown to reduce degradant levels to < 0.15 total area % (HPLC, λ 254 nm) and extend production intervals to the original 72-hour target in a commercial-scale unit with a nameplate capacity of 800 kg/hr.

    The benzothiazolinone ring is susceptible to hydrolysis under alkaline process liquors encountered during reactor clean-out. Exposure of residual benazolin technical to 2% sodium hydroxide solution at 80°C for 60 minutes opens the thiazole ring, yielding 4-chloro-2-sulfanylphenylacetic acid and formic acid as the terminal breakdown products. Wastewater streams containing this ring-opened intermediate exhibit Chemical Oxygen Demand (COD) values exceeding 12,000 mg/L and require dedicated oxidative treatment with Fenton’s reagent (FeSO4·7H2O at 500 mg/L and H2O2 35% at 1.5 mL/L) at pH 3.0 for 4 hours to reduce COD to below local discharge consent limits of 800 mg/L. Facilities handling benazolin in multi-purpose plants must segregate alkaline wash streams from general wastewater collection until analytical verification of ring-intact compound absence is confirmed by HPLC-DAD.

    Storage in humidity-controlled, ventilated warehouses at temperatures not exceeding 30 °C and relative humidity below 60% is prescribed; deviation above 65% RH for 21 days results in caking and a measurable shift in the melting endotherm peak to 188 °C (DSC, 10 K/min heating rate) associated with hydrate formation at the crystal surface. The re-dried material, while chemically within specification, exhibits reduced milling efficiency, requiring a 15–20% increase in bead-mill residence time to re-attain the target particle size for SC production.