Isothiazole

Isothiazole


    • Product Name Isothiazole
    • Alias 1,2-Thiazole
    • Einecs 207-726-8
    • Mininmum Order 1Gram
    • Factory Site West Ujimqin Banner, Xilingol League, Inner Mongolia, China
    • Price Inquiry sales9@bouling-chem.com
    • Manufacturer Bouling Chemical Co., Limited
    • CONTACT NOW
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    Specifications

    HS Code

    160891

    Chemical Formula C3H3NS
    Molar Mass 85.12 g/mol
    Appearance Colorless to pale yellow liquid
    Odor Pungent
    Boiling Point 144 - 145 °C
    Melting Point -38 °C
    Density 1.129 g/cm³
    Solubility In Water Slightly soluble
    Solubility In Organic Solvents Soluble in many organic solvents
    Stability Stable under normal conditions
    Flash Point 43 °C
    Acidity Weakly acidic

    As an accredited Isothiazole factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing Isothiazole in 5 - kg sealed containers, ensuring secure chemical packaging.
    Shipping Isothiazole is a chemical that may have specific shipping regulations due to its nature. It should be packaged securely in appropriate containers, labeled clearly, and shipped following hazardous materials guidelines to ensure safe transit.
    Storage Isothiazole should be stored in a cool, dry, well - ventilated area, away from heat sources and open flames to prevent ignition. It should be kept in a tightly - sealed container to avoid contact with air and moisture, which could potentially lead to degradation or reactivity. Store it separately from oxidizing agents and other incompatible substances to ensure safety.
    Application of Isothiazole

    Can Isothiazolinones Maintain Emulsion Integrity in High-Pressure Metalworking Fluid Systems?

    The recirculating coolant sumps of high-speed CNC machining centers, operating at pressures above 70 bar and sump volumes exceeding 5,000 L, present a continuous inoculation challenge where tramp oil phases stabilize Pseudomonas fluorescens and Mycobacterium immunogenum biofilms. A 20% active benzisothiazolinone (BIT) sodium salt solution—selected for its non-volatility and stability above pH 9.0—is metered into the return line via a diaphragm dosing pump at a rate calibrated to maintain a residual active concentration of 80–150 ppm in the bulk fluid, as verified by HPLC-UV against a calibration curve built with the NIST SRM 2133 reference. Field data from a central system treating 20,000 L of water-dilutable semi-synthetic fluid, logged with an AT-line ATP bioluminescence monitor (Hygiena EnSURE Touch), show that when the free BIT level drops below 52 ppm for more than 72 hours, the relative light unit (RLU) count escalates from a baseline of < 50 RLU to above 2,500 RLU, correlating with a pH crash from 9.2 to 6.7 and a visible split of the oil-water emulsion. Compliance is structured around TRGS 611 (Technical Rules for Hazardous Substances) in Germany—requiring a maximum 3-(3,4-dichlorophenyl)-1,1-dimethylurea (diuron)-equivalent hazard index of < 1—and the EU BPR product-type 13 (metalworking fluid preservatives), where the BIT active substance inclusion in the Union List is conditioned on a total aerobic biodegradability of > 60% in 28 days per OECD 301B. The dosed concentrate is formulated with a co-dispersant such as a 1.5 wt% sodium polynaphthalene sulfonate to prevent flocculation when mixed with calcium-containing water hardness above 400 ppm CaCO₃. Post-biocide addition, the fluid undergoes a 20-minute dwell in a clean-side weir tank before reaching the cutting zone, ensuring complete dissolution and minimizing the risk of stray aerosol mists exceeding the 0.2 mg/m³ inhalable fraction occupational exposure limit referenced in the MAK Collection. Terminal metal parts—such as transmission valve bodies milled from AlSi7Mg0.3 alloy—are subsequently washed in an alkaline cleaner at pH 10.5 at 60°C; any residual BIT carryover must remain below 2 μg/cm² on the substrate surface to satisfy the paint adhesion specification DIN EN ISO 2409:2013 cross-hatch rating of ≤ 1. A known failure mode emerges when BIT is co-dosed with an amine-based corrosion inhibitor package containing monoethanolamine borate: the free amine catalyzes an intramolecular rearrangement of BIT to 2-mercaptobenzamide, a species with 10-fold lower antimicrobial activity, detectable via a characteristic UV shift from 272 nm to 245 nm in the fluid’s absorbance spectrum.

    Preservation of in-can waterborne architectural coatings against sulfate-reducing Desulfovibrio and cellulolytic Chaetomium globosum is achieved through the post-pigment-dispersion introduction of a 2.5 wt% mixture of 2-methyl-4-isothiazolin-3-one (MIT) and 1,2-benzisothiazolin-3-one (BIT) at a ratio of 1:4, targeting a combined active loading of 95–125 ppm relative to the final wet paint. The addition step must be executed in the letdown vessel at a pH window of 7.8–8.5 and at a temperature below 38°C; excursions above this thermal threshold accelerate the hydrolysis of the isothiazolinone ring, with the pseudo-first-order rate constant increasing from 8.7×10⁻⁴ h⁻¹ at 25°C to 4.2×10⁻² h⁻¹ at 45°C as determined by isothermal microcalorimetry imitating ASTM E2070-23 methodology. The inoculation resistance is evaluated through a triple-challenge protocol per ASTM D2574-16, requiring plate counts below 10 CFU/mL for Pseudomonas aeruginosa ATCC 9027 and Escherichia coli ATCC 8739 after 7-day incubation at 30°C. The cured semigloss film further meets the EN 15457:2014 fungal resistance rating of 0 (no visible growth) when the isothiazolinone in-can package is supplemented with 0.3% zinc pyrithione (ZPT) as a dry-film co-biocide; the partition coefficient of MIT between the aqueous phase and the coalescing latex binder—measured by equilibrium dialysis—dictates that approximately 18% of the initial biocide remains sequestered in the dried polymer matrix, creating a long-term surface depletion boundary observable via ToF-SIMS depth profiling. Regulatory alignment with the EU Ecolabel for indoor paints (Commission Decision 2014/312/EU) prohibits isothiazolinone concentrations that contribute more than 0.050% of the total wet product weight, and the finished coating must emit less than 0.010 mg/m³ of total isothiazolinones in chamber air after 3 days per ISO 16000-9:2006. In markets requiring GB 18582-2020 conformity, the sum of MIT and CMIT in the packaged paint cannot exceed 15 mg/kg, a threshold that forces formulators to rely almost exclusively on BIT for premium interior products. The packaged product exits the filling line in 10 L HDPE pails with a nitrogen-blanketed headspace, reducing dissolved oxygen to below 0.5 mg/L and effectively eliminating aerobic spoilage organisms even in the event of temporary biocide underdosing during a shift change.

    When Rinse-off Limits Reach 15 ppm: Navigating Isothiazolinone Preservation in Leave-on vs. Wash-off Personal Care Matrices

    The EU Cosmetics Regulation 1223/2009 Annex V entry for the CMIT/MIT (3:1) mixture confines its use to rinse-off products at a maximum active concentration of 15 ppm, and pure MIT is capped at 100 ppm in the same product category under entry 57. In a typical conditioning shampoo containing 12 wt% sodium laureth sulfate and 3 wt% cocamidopropyl betaine, post-dosing of a 1.5% MIT solution to achieve 85 ppm active MIT results in a preservative efficacy meeting criterion A of ISO 11930:2019—specifically, a 3-log reduction for Staphylococcus aureus ATCC 6538 within 7 days and no recovery by day 28—provided the surfactant micelles do not sequester more than 22% of the biocide, as quantified by centrifugal ultrafiltration coupled with LC-MS/MS. Formulators targeting the COSMOS-standard for natural cosmetics cannot deploy halogenated isothiazolinones (CMIT is prohibited) but may resort to BIT at a maximum recommended concentration of 0.1%, though sensitization data from the IVDK (Information Network of Departments of Dermatology) indicate a patch test positivity rate of 2.3% for BIT in Central European populations, triggering obligatory labeling under Article 19 of the Cosmetics Regulation whenever the threshold exceeds 0.001% in leave-on and 0.01% in rinse-off products. Manufacturing process controls demand that the biocide be introduced into the cooled aqueous phase at < 35°C after neutralization of the carbomer rheology modifier to pH 6.8; the subsequent high-shear homogenization at 3,500 rpm must not raise the batch temperature above 38°C, else the MIT degradation pathway accelerates, generating N-methyl-3-mercaptopropionamide, a sensitizer detectable via a M+H⁺ ion at m/z 148.2 in the product’s LC-QTOF chromatogram. The final packaged unit—a 250 mL PET flip-top bottle—undergoes a 45°C accelerated stability challenge over 12 weeks, with active MIT content required to remain within 90–110% of label claim; formulators frequently add 0.02% tetrasodium EDTA as a potentiation agent to chelate iron ions that otherwise catalyze isothiazolinone oxidation via a Fenton-type mechanism. The finished product must simultaneously satisfy ASEAN Cosmetic Directive Annex VI for markets in Southeast Asia, where MIT limits in rinse-off are aligned with the EU but additional country-specific notifications apply, such as the requirement for a BPOM registration in Indonesia with a detailed compositional disclosure of all isothiazolinone species down to 10 ppm level.

    Biofouling abatement in polyamide thin-film-composite reverse osmosis membranes—installed in train configurations producing 300 m³/h of ultrapure water for semiconductor wafer rinsing—is executed through a cyclical shock-dosing protocol of 2,2-dibromo-3-nitrilopropionamide is not relevant here; instead, a 20% active BIT dispersion stabilized with 0.5% xanthan gum is injected into the feed stream to maintain a concentration of 50 mg/L as total BIT for a 45-minute contact period once every 72 hours. The compatibility threshold with the membrane’s polyamide barrier is verified by monitoring salt rejection per ASTM D4194-23: a drop from 99.6% to below 99.0% NaCl rejection within 1,000 hours of cumulative BIT exposure at pH 8.2 signals incipient amide bond hydrolysis; field data from a 7-element vessel supplied by Toray TM720D-400 elements indicate that the critical cumulative BIT contact limit is approximately 3,200 ppm·h before the membrane warranty clause is triggered. The dosed concentrate is drawn from an IBC tote via a peristaltic pump equipped with EPDM tubing resistant to BIT-induced embrittlement, and the injection quill is positioned 5D upstream of the cartridge filter housing to guarantee radial mixing before the high-pressure pump suction. Compliance with NSF/ANSI 60 (drinking water treatment chemicals) mandates that the BIT source achieve a minimum purity of 98.5% with dibenzothiazyl disulfide impurity limited to < 0.2%, and that the maximum use level not exceed 10 mg/L in the permeate, verified via quarterly extraction and analysis by EPA Method 527. The permeate side is continuously monitored for TOC via a Sievers M9 analyzer; an excursion above 1.2 ppb total organic carbon during biocide slugging initiates an automatic diversion to the reject recovery loop. Finished ultrapure water delivered to the point-of-use immersion lithography tool must conform to SEMI F63-0523 specification for anion and cation contaminants with BIT-derived carbon accounting for less than 0.05 ppb. The concentrated reject stream, carrying spent BIT at 150–200 mg/L, is treated via UV/H₂O₂ advanced oxidation at 254 nm with 35 mg/L hydrogen peroxide to achieve > 99% abatement of the heterocyclic ring before discharge to the municipal collection system, as prescribed by the local indirect discharge permit’s acute Daphnia magna 48-h EC₅₀ value of 0.6 mg/L for BIT.

    Adhesive Emulsion Preservative Trapping in High-Filler Formulations

    Vinyl acetate-ethylene (VAE) copolymer emulsions formulated for D3 wood bonding (per EN 204/205) and containing 45–55% calcium carbonate filler exhibit a preservative demand that deviates markedly from the neat emulsion due to the high specific surface area (ca. 12 m²/g BET) of the carbonate particles, which adsorbs up to 35% of a dosed CMIT/MIT blend within the first 4 hours of mixing at 23°C, as demonstrated by depletion isotherm experiments fitted to the Freundlich model with KF = 0.87 and 1/n = 0.62. To compensate, the typical dose of a 1.5% CMIT/0.5% MIT commercial formulation is raised from the standard 0.15% to 0.25% on total product mass, delivering an active total of 50 ppm isothiazolinone; the preservative is added after the filler has been fully wetted and the temperature has fallen below 30°C, using a side-entry agitator running at 250 rpm to avoid vortex formation that could entrain oxygen and catalyze the oxidative coupling of MIT to its disulfide dimer, identifiable as an additional peak in the UV chromatogram at retention time 12.8 min. Quality control relies on EN 152:2011 challenge tests with Aspergillus brasiliensis ATCC 16404 and Burkholderia cepacia ATCC 25416—the latter being a notorious biofilm former in the adhesive industry—with a pass defined as < 10 CFU/g after 28 days, even when the infected filler raw material contributes an initial bioburden of 10⁴ CFU/g. Products destined for food-contact packaging adhesives fall under BfR Recommendation XXXVI (Paper and board for food contact) or the U.S. 21 CFR 176.170 (Components of paper and paperboard in contact with aqueous and fatty foods), where the specific migration limit for total isothiazolinones must not exceed the detection limit of 0.05 mg/kg food simulant when tested according to EN 1186-1:2002 migration protocols; consequently, only BIT—which exhibits a molecular weight of 151.2 g/mol and a log Pow of 1.3 making it less prone to fatty simulant migration—is preferred for such applications at a dose capped at 0.10%. The filled emulsion is packaged in 1000 L IBCs with an integral dip tube made of PVDF to resist solvent welding by residual vinyl acetate monomer; a blanket of nitrogen (99.5% purity) is maintained at 50–100 mbar overpressure during the 48-hour filling operation to suppress aerobic metabolism. Spot-test monitoring of the adhesive for hydrogen sulfide—a metabolic product of sulfate-reducing contaminants—using lead acetate paper strips is conducted at each shift handover; a positive result triggers an immediate top-up dose of 0.05% CMIT/MIT, injected via a sanitized dosing lance, with full traceability logged into the plant’s ISO 9001:2015 batch record system.

    Control of Leptothrix-dominated biofilm and endospore-forming Bacillus species in the closed white-water circuits of recycled containerboard mills is achieved through continuous addition of a 10% BIT alkaline dispersion to the machine chest at a rate of 150–250 g of formulated product per tonne of bone-dry fiber, equivalent to a residual soluble BIT level of 12–18 mg/L in the white-water tray, as measured daily by a Merckoquant test strip cross-validated with HPLC. The high filler content of the process water—ash levels often exceed 35% on a dry basis—demands that the biocide be fed through a 316L stainless steel static mixer just after the primary hydrocyclone cleaner, ensuring dispersion before contact with the cationic retention aid (0.03% polyDADMAC) that otherwise precipitates BIT through electrostatic bridging, reducing efficacy by up to 60% within 30 seconds. The microbial challenge is monitored using ATP analysis and qPCR targeting the 16S rRNA gene; a threshold of 10⁴ gene copies/mL in the headbox slurry triggers an automatic escalation to 300 g/ton BIT. End-product compliance for paper intended for dry foodstuff packaging is assessed under BfR XXXVI/1 conditions, with a chloroform extraction of the paper followed by GC-MS quantification per EN 645 adapted method—total BIT plus any degradation-derived benzothiazole must remain below 0.5 mg/dm² of paper surface. The finished linerboard, reeled at 1,200 m/min, is immediately stretch-wrapped to prevent atmospheric re-contamination; a quarterly audit of the water system includes culturing for Legionella species per ISO 11731:2017 because the warm (42°C) white-water loop creates a niche for proliferation. Where the mill achieves zero liquid discharge status, the accumulation of non-biodegradable BIT in the recirculated water can attain concentrations above 45 mg/L after 6 months of continuous operation, requiring a side-stream treatment using granular activated carbon (Filtrasorb 400) columns with an empty bed contact time of 15 minutes to strip the isothiazolinone and prevent inhibition of the downstream anaerobic sulfite-reducing bacteria in the closed-loop wastewater treatment digester.

    Textile Padder Application and the Dichotomy of Antibacterial Efficacy vs. Skin Sensitization

    A 20% active proprietary formulation of 2-n-octyl-4-isothiazolin-3-one (OIT) is employed on a continuous padding mangle at 30 m/min to impart antibacterial finish to polyester nonwoven mattress ticking, targeting an add-on of 0.8–1.2% OIT by weight of fabric after thermofixation at 150°C for 90 seconds in a stenter frame. The pad liquor, prepared with 8 g/L of the OIT dispersion and 1 g/L of an ethoxylated wetting agent (HLB 13.5), must be maintained at pH 5.5–6.0 using a 300 mM citrate buffer because OIT is susceptible to nucleophilic attack by hydroxyl ions at the alkaline pH values typical of scoured textiles, yielding 2-octyl-4-mercaptothiazole—a species with no biocidal activity detectable by the JIS Z 2801:2010 (now ISO 22196:2011) test for antibacterial activity on plastic surfaces, adapted for textiles. After the padded fabric exits the stenter, it is allowed to cure for 48 hours post-production to complete the diffusion of OIT into the polyester amorphous regions; the final surface concentration is verified by solvent extraction with methanol and subsequent GC-FID quantification against a standard solution traceable to NIST SRM 1968. Efficacy testing must demonstrate a > 99.9% (3-log) reduction of Staphylococcus aureus ATCC 6538P and Klebsiella pneumoniae ATCC 4352 after 24-hour contact according to AATCC 100-2019. However, a persistent limitation is sensitization: OIT has been classified as a skin sensitizer in the ECHA harmonized classification and labeling (CLP) Annex VI with the hazard statement H317, and the OEKO-TEX Standard 100 class II (direct skin contact) recognizes a permissible limit of 25 ppm total extractable OIT, tested per the EN ISO 17075:2008 method. To meet this, post-cure washing on a 10-bowl open-width washing range with counter-current flow at 60°C and a residence time of 4 minutes per bowl is necessary to leach out unbound OIT, reducing the residual from an initial 800 ppm to below the 25 ppm threshold, a process monitored inline by a UV-reflectance sensor. The washed fabric is then dried on steam-heated cylinders and wound into rolls for cutting and sewing; the final mattress protector is labeled with an explicit caution to discontinue use if skin irritation develops, a requirement triggered by the EU General Product Safety Directive (2001/95/EC) when residual OIT exceeds 10 ppm.

    The maintenance of hygienic conditions in automatic scrubber-drier detergent concentrates—typically a 10X dilution of nonionic surfactants (alcohol ethoxylates, C9–C11 chain, 8 EO units), builder agents (sodium citrate dihydrate, 5 wt%), and fragrance—relies on a dual-isothiazolinone system combining 0.05% BIT with 0.005% MIT, achieving a cost-optimized spectrum of activity against Pseudomonas putida and Aspergillus niger while maintaining the formulation’s clarity at storage temperatures as low as 5°C. The addition sequence is critical: the isothiazolinones are pre-diluted in the surfactant phase before the addition of the chelator to avoid early-phase precipitation with divalent ions present in the city water (250–350 ppm total hardness). A six-month storage test at 25°C with weekly viable counts per EN 13697:2015 for bactericidal and fungicidal activity on hard surfaces confirms that the combination sustains a pass level (> 5-log reduction for bacteria, > 4-log for fungi) through five iterative re-inoculations, provided the pH remains within 6.0–7.5. Above pH 8.0, the MIT component loses 30% of its initial activity within 90 days due to ring opening, monitored by a UV–vis spectral shift at 274 nm. Compliance under the EU Detergent Regulation (EC) No 648/2004 requires that any isothiazolinone present above 0.0015 wt% be declared on the label with the designated allergen phrase for MIT or CMIT/MIT, while finished product classification must align with the CLP risk assessment, especially regarding eye damage (H318) if the total active exceeds a pH-dependent partition coefficient threshold. The packaged product, a 5 L high-density polyethylene jerrican with a polypropylene screw cap, is equipped with a metering pump for automatic dilution to a 1:100 ready-to-use solution delivered onto floor surfaces; the ready-to-use solution retains an active MIT+BIT concentration of 5.5 ppm, sufficient to achieve a 99.9% kill of Listeria monocytogenes in a 5-minute contact time according to the ASTM E1153-22 quantitative carrier test for food-processing plant sanitation, providing an extended application beyond household cleaning into light industrial disinfection.

    Table 1 — Typical Isothiazolinone Active Substance Ranges in Selected Technical Applications
    Application MatrixBIT (ppm)MIT (ppm)CMIT/MIT 3:1 (ppm)OIT/DCOIT (ppm)Critical pH Window
    Latex paint in-can50–12015–307–217.5–9.0
    Metalworking fluid (semi-synthetic)80–15010–30 (shock)8.8–9.5
    RO membrane biocide50 (slug)5–15 (DCOIT)7.0–8.5
    VAE adhesive emulsion80–1205–1520–504.5–7.0
    Rinse-off shampoo< 10085–100< 155.5–7.0
    Paper mill white-water12–18 mg/L6.5–8.0
    Textile pad finish300–500 (OIT)5.0–6.5
    Hard-surface cleaner concentrate500 (as product)50 (as product)6.0–8.0
    Table 2 — Key Regulatory and Test Standard References Per Application Sector
    Industry SectorPrimary Regulation/DirectiveEfficacy Test StandardMigration/Emission Standard
    Architectural CoatingsEU BPR PT6, GB 18582-2020ASTM D2574-16ISO 16000-9:2006
    Metalworking FluidsTRGS 611, BPR PT13ASTM E2275-19MAK inhalable aerosol ≤0.2 mg/m³
    Reverse Osmosis WaterNSF/ANSI 60, SEMI F63EPA Method 527 (permeate)
    AdhesivesBfR XXXVI, 21 CFR 176.170EN 152:2011EN 1186-1:2002
    Personal CareEC 1223/2009 Annex VISO 11930:2019Sensitizer label per Article 19
    Paper & BoardBfR XXXVI/1, FDA 176.170ISO 11731:2017 (monitoring)EN 645 (extraction < 0.5 mg/dm²)
    TextilesOEKO-TEX 100, CLP Annex VIAATCC 100-2019EN ISO 17075 (OIT leachable ≤25 ppm)
    Cleaning ProductsDetergent Reg. 648/2004EN 13697:2015Allergen declaration > 15 ppm
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    Isothiazole derivatives, predominantly 3-isothiazolinones substituted at the 2- and 5-positions, constitute a class of heterocyclic biocides employed across aqueous industrial formulations to control bacteria, fungi, and algae. The most commercially significant variants are 5-chloro-2-methyl-4-isothiazolin-3-one (CMIT, CAS 26172-55-4), 2-methyl-4-isothiazolin-3-one (MIT, CAS 2682-20-4), 1,2-benzisothiazolin-3-one (BIT, CAS 2634-33-5), and 2-octyl-4-isothiazolin-3-one (OIT, CAS 26530-20-1). A common commercial presentation is a 1.5% (w/w) aqueous solution of CMIT/MIT in a 3:1 ratio, stabilized with 0.15% copper nitrate and 2.5% magnesium nitrate; BIT is often supplied as a 20% active dispersion, while OIT appears as a 45% solution in a glycol ether carrier. Molecular action proceeds through electrophilic attack on intracellular thiols, forming mixed disulfides with glutathione and enzyme-active cysteine residues, thereby disrupting redox homeostasis and proton motive force. Specification parameters for the 1.5% CMIT/MIT blend include a density of 1.15–1.20 g/cm³ at 25°C (ISO 2811-1:2016), a pH of 2.0–4.0, and a freezing point near −4°C. Potency is quantified via minimal inhibitory concentration (MIC) against Pseudomonas aeruginosa ATCC 9027 using ISO 11930:2012 broth dilution, with values typically 5–15 ppm active ingredient for CMIT and 100–200 ppm for BIT.

    Comparative Properties of Isothiazole Biocides versus Alternative Preservative Chemistries
    Active SubstanceCAS No.Typical In-Can Dosage (w/w active)MIC P. aeruginosa (ISO 11930)pH Stability WindowMode of ActionNotable Regulatory Restriction
    CMIT/MIT (3:1)26172-55-4 / 2682-20-40.05–0.15%5–15 ppmpH 2–9Electrophilic thiol oxidationSkin Sens. 1 (H317), CLP Annex VI; EU BPR PT 6, 11–13 approved
    BIT2634-33-50.1–0.3%100–200 ppmpH 4–12Thiol-disulfide exchangeClassified Skin Sens. 1; restricted in aerosol-generating applications per REACH
    OIT26530-20-10.2–0.5% (dry film)20–50 ppm (fungal)pH 5–10Membrane thiol disruptionBanned in EU from use in indoor paints with skin contact potential (EU 2018/1480)
    Bronopol (2-bromo-2-nitropropane-1,3-diol)52-51-70.02–0.1%25–50 ppmpH 5–8 (nitrosamine risk below pH 4)Thiol oxidation + membrane damageNitrosamine formation potential under acidic storage regulated under ICH M7
    DBNPA (2,2-dibromo-3-nitrilopropionamide)10222-01-20.01–0.05%2–8 ppmpH 6–8.5; rapid hydrolysis above pH 9Rapid bromide release inhibits respirationShort half-life in alkaline systems limits use to quick-kill preservative only
    Formaldehyde donor (tris(hydroxymethyl)nitromethane)126-11-40.1–0.3%80–160 ppmpH 6–10; formaldehyde release drops sharply below pH 6Protein crosslinking and alkylationFormaldehyde reclassified as Carc. 1B (EU 605/2014); indoor emission limits per ISO 16000-3

    In recirculating central sump systems processing ferrous alloys with sulfurized extreme-pressure additives, the biocidal efficacy of isothiazolinones confronts multiple deactivation pathways. A 10,000 L central sump equipped with belt oil skimmers and a high-pressure coolant delivery manifold operating at 1.2 m³/h flow may experience a pH drift from 8.8 to 9.4 within 48 h due to alkaline cleaner carry-over. Under these conditions, the half-life of CMIT at 40°C falls below 16 h, as determined by HPLC monitoring of active content per ASTM E2409-13. If the sump pH exceeds 9.3, Pseudomonas aeruginosa blooms can surpass 10⁷ CFU/mL in the same interval, measured by dip-slides under ASTM E2169-17. To maintain control, metalworking fluid formulators frequently substitute BIT at 0.15–0.2% active addition to the concentrate, owing to its superior high-pH stability: long-term immersion tests at pH 9.5 and 35°C following ISO 6743/7 fluid classification show BIT retains >80% residual activity after 14 days. A major processing conflict arises when mercaptobenzothiazole (MBT) corrosion inhibitors are co-formulated: the thiol moiety of MBT undergoes nucleophilic displacement with the isothiazolinone sulfur, forming an inactive heterocyclic adduct. Production-scale batch records confirm that separate addition points—BIT post-emulsification, MBT introduced later at a temperature below 45°C—reduce potency loss from 30% to less than 5% over a 6-month shelf life, as verified by ASTM E645-18 challenge tests. Clarified emulsion particle size distributions must stay within 0.8–1.5 µm Dv50 to avoid biocide sequestration inside swollen micelles.

    Architectural Coating Preservation — Mitigating In-Can Spoilage During High-Shear Dispersion and Storage

    Preservation of high-PVC interior matt paints based on vinyl acetate-ethylene (VAE) emulsions demands careful attention to biocide-pigment interactions. Addition of a 1.5% CMIT/MIT solution at 0.10–0.18% (w/w of wet paint) must occur after the pigment dispersion and let-down stages, because thermal input from a high-speed dissolver with a tip speed of 18–22 m/s can elevate batch temperature above 60°C, accelerating hydrolytic degradation of the isothiazolinone ring. In a 500 kg production vessel, post-addition blending at 300 rpm for 15 minutes achieves homogeneous distribution without inducing micro-foam, confirmed by active content analysis via HPLC with UV detection at 280 nm per ASTM D5586-21. The preserved paint must withstand repeated inoculation with a mixed consortium of Pseudomonas aeruginosa, Enterobacter cloacae, and Aspergillus brasiliensis per ISO 11930:2012, with acceptance criteria of <10 CFU/g at day 7 and no recovery at day 28. A known failure mode emerges when associative thickeners of the hydrophobically modified ethoxylated urethane (HEUR) type are present: certain HEUR grades carry residual sulfhydryl-terminated oligomers that deactivate CMIT on storage, leading to a biocide half-life of only 3–4 weeks at 40°C in contrast to the typical 6 months in non-associative cellulosic-thickened systems. Therefore, lot-specific compatibility screening with shear-storage cycling (1 week at 50°C, ASTM D1849-95(2023)) is mandated. For dry-film protection against algal colonization, OIT is introduced at 0.3–0.5% active on binder solids, tested by EN 15458:2022 blue stain resistance; here the temperature ceiling during incorporation must not exceed 40°C to avoid premature volatilization.

    How Do Isothiazolinone-Based Actives Differ from Formaldehyde-Releasing Biocides in Terms of pH-Dependent Stability and Spectra of Activity?

    Unlike formaldehyde-depot biocides that rely on a slow equilibrium release of the active aldehyde species, isothiazolinones operate through direct electrophilic attack on intracellular thiols. This mechanistic distinction yields a divergent pH-efficacy profile: CMIT/MIT maintains full bactericidal capacity up to pH 8.5 but loses > 90% of its Pseudomonas-killing activity above pH 9.2 at 30°C within 24 h, as measured by log-reduction assays under EN 1040:2005. Formaldehyde donors such as tris(hydroxymethyl)nitromethane exhibit more gradual decline, retaining 40–50% efficacy at pH 9.5 over the same period, though their activity drops precipitously below pH 6 as formaldehyde liberation becomes kinetically limited. The microbiocidal spectrum also differs: isothiazolinones are highly efficacious against Gram-negative bacteria at low concentrations (MIC < 15 ppm for CMIT) but demonstrate weaker control of sulfate-reducing bacteria (SRB) unless BIT is selected, whereas formaldehyde donors provide broader, albeit slower, suppression of anaerobes. In metalworking fluid practice, switching from a triazine-based formaldehyde donor to a BIT/MIT combination reduces the frequency of Mycobacterium immunogenum outbreaks, documented in field trials where sump counts fell from 10³ CFU/mL to <10 CFU/mL within 72 h after a single BIT dose of 500 ppm active. A critical operational limitation of isothiazolinones remains their incompatibility with strong reducing agents and sulfides: the presence of hydrogen sulfide at 0.5 ppm in contaminated process water causes irreversible ring-opening, whereas formaldehyde-based biocides are unaffected by sulfide taint. Therefore, plant water quality specifications must stipulate sulfide content <0.1 ppm (ISO 13358:1997) before isothiazole injection.

    When OIT Is the Preferred Dry-Film Fungicide in Exterior Silicone Emulsion Paints

    Exterior façade paints formulated with silicone resin-modified acrylic binders demand a dry-film fungicide that resists ultraviolet photolysis and does not migrate to the surface as efflorescence. In accelerated weathering trials (ISO 16474-3:2021, Method A, 2000 h Xenon-arc), OIT at 0.4% (active on total film weight) yielded a 97% suppression of Cladosporium cladosporioides growth versus 64% for an equimolar loading of carbendazim, with no observable chalking or color shift above ΔE* 1.5. OIT’s octanol-water partition coefficient (log Kow 2.8) limits aqueous extraction, keeping leaching rates below 0.02 mg/m² per rainfall cycle in a 48 h dynamic leaching test per CEN/TS 16637-2:2014. However, regulatory constraints must be acknowledged: EU Biocidal Products Regulation (BPR, PT 7) approval for OIT in exterior coatings remains valid only where skin contact is incidental, and labeling under CLP requires the EUH208 statement due to sensitization potential. Production-scale tinting systems that use iron oxide pigment pastes containing residual surfactant levels above 2% on pigment weight can interfere with OIT crystallinity in the dried film, reducing its biocidal availability by up to 30% (confocal Raman mapping data). Consequently, formulators pre-mix OIT with a coalescent such as texanol at a 1:2 ratio before let-down to ensure molecular dispersion and uniform film distribution.

    A separate preservation niche exists in spiral-wound reverse osmosis membrane storage. After chemical cleaning with alkali or acid, membranes must be flushed with a preservative solution to prevent biofilm growth during standby. A 0.05% (v/v) dosing of a 1.5% CMIT/MIT blend provides > log 4 reduction of planktonic bacteria within 30 min (ASTM E2315-16 time-kill procedure). The solution is recirculated at 0.5 m/s cross-flow velocity for 20 min and left static for up to 30 days. However, isothiazolinone residual must be completely purged with permeate until HPLC-detectable levels fall below 0.1 ppm before resuming production, because CMIT adheres to polyamide barrier layers and can cause a temporary rejection drop of 2–5% if not flushed. Published data for this specific membrane configuration is limited, but field reports from two-pass seawater desalination trains indicate that a rinse volume of the element dead volume is sufficient to restore nominal salt passage. Any oxidative disinfection step (e.g., chlorine at 0.5 ppm free residual) must be separated from isothiazole preservation by a dechlorination stage using sodium bisulfite to avoid instant oxidative degradation of the biocide.

    Compliance and Standard Reference Matrix for Isothiazole Biocide Products
    Standard/RegulationScopeProduct Conformity Parameter
    ISO 11930:2012Evaluation of preservation efficacy in cosmetic and industrial fluidsProtocol for challenge-test validation of CMIT/MIT and BIT in metalworking fluids and paints
    ASTM D5586-21Determination of CMIT/MIT in water-based paints by HPLCAcceptable active retention ≥ 85% after 12 months at 25°C
    EN 15458:2022Test method for resistance of coatings to algal growthOIT dry-film loading ≥ 0.3% passes zone-of-inhibition criteria
    ASTM E2169-17Microbial dip-slide monitoring in metalworking fluidsBulk fluid count maintained <10³ CFU/mL with BIT at 150 ppm active
    EU BPR (528/2012)Biocidal product authorization for PT 6 (in-can preservatives), PT 11 (liquid cooling and processing systems), PT 12 (slimicides)Active substance listed in Annex I; product must comply with specific conditions per letter of authorization
    CLP (EC 1272/2008)Classification, labelling, and packaging of substances and mixturesCMIT/MIT ≥ 0.0015% triggers Skin Sens. 1; OIT ≥ 0.05% triggers EUH208
    ISO 16000-3:2011Indoor air determination of formaldehyde emission; relevant for comparison to formaldehyde-free isothiazole useIsothiazole-preserved interior paints do not contribute to formaldehyde TVOC, meeting low-emission certification criteria
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