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Store “2',6'-Diobromo - 2 - Methyl - 4'-Trifluoromethyox - 4 - Trifluoromethyl - 1,3 - Thiazole - 5 - Carboxanilide” in a cool, dry, well - ventilated area. Keep it away from heat sources, direct sunlight, and incompatible substances. Use tightly - sealed containers to prevent moisture absorption and ensure the integrity of the chemical to maintain its stability and quality.
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2',6'-Diobromo-2-Methyl-4'-Trifluoromethyox-4-Trifluoromethyl-1,3-Thiazole-5-Carboxanilide is manufactured under an ISO 9001 quality system and complies with relevant regulatory requirements.
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More Introduction
What Distinguishes This Molecule from First-Generation Carboxanilides?
The introduction of a trifluoromethoxy substituent at the 4′-position of the aniline ring is the structural determinant setting thifluzamide apart from older carboxin derivatives and from the majority of later-generation SDHIs such as boscalid or penthiopyrad. This group elevates the octanol-water partition coefficient sufficiently to enable rapid cuticular penetration without sacrificing phloem mobility; translocation assays on rice plants using ¹⁴C-labeled material have demonstrated acropetal movement with 12–18% of applied radioactivity reaching the third leaf above the treatment zone within 48 hours. In contrast, boscalid (log P ≈ 2.9) and isopyrazam (log P ≈ 4.4) occupy different lipophilicity spaces and consequently exhibit sharply divergent distribution kinetics across the leaf epidermis-mesophyll continuum. Furthermore, the 2′,6′-dibromo substitution pattern contributes to metabolic stability against oxidative debromination by CYP450 monooxygenases, a detoxification route that compromises the persistence of certain monohalogenated carboxanilides in cereal crops. Hydrolytic stability data (OECD 111) indicate a half-life exceeding 30 days at pH 5, 7, and 9 (40 °C), confirming that the trifluoromethoxy ether linkage is resistant to base-catalysed cleavage under conditions typical of tank-mix solutions buffered to pH 6–8.
Sheath Blight Control in Direct-Seeded Rice: Operational Envelope and Granular Formulation Constraints
Application to rice culture, the primary volume driver for thifluzamide globally, demands strict adherence to a processing window defined by the reproductive stage of the crop. The product is most frequently deployed as a suspension concentrate (SC) containing 240 g a.i./L or as 0.5% and 1.5% granule (GR) formulations for paddy water application. In transplanted systems, a single broadcast of 15 kg/ha of 1.5% GR (225 g a.i./ha) at 5–7 days before panicle initiation provides 21–28 days of protective activity against AG-1 IA, with a suppression rate consistently above 85% in trials conducted under IRRI standard evaluation protocol (SES, 2013). The granular formulation must achieve a water-dispersal profile that releases ≥ 80% of the nominal active within 3 hours of submergence; this is routinely verified by CIPAC MT 176 rotating cylinder method at 30 rpm in standard 500 ppm hard water. Failure to meet the 3-hour dissolution benchmark, often resulting from over-compaction during pan granulation with bentonite carriers, leads to localized phytotoxicity on emerging flag leaves because undispersed granules create continuous exposure points on the leaf sheath.
In direct-seeded systems where flooding is delayed, a 240 g/L SC is applied by foliar spray at 200–300 mL/ha (equivalent to 48–72 g a.i./ha) when disease incidence reaches 5% tiller infection. Nozzle selection is non-trivial: hollow-cone nozzles delivering 200–250 µm volume median diameter (VMD) droplets maximize deposition on the vertical leaf sheath, whereas air-induction nozzles (VMD > 400 µm) reduce coverage on lower canopy strata and have been associated with 12–17% lower efficacy in LSU AgCenter trials (2019). The SC formulation must maintain a suspension stability index ≥ 0.95 after 30 minutes in CIPAC standard water D (CIPAC MT 184.1) and exhibit a pourability residue below 2.5% after rinsing. Milling the technical material in a horizontal bead mill (Netzsch MiniCer, 0.3 mm yttria-stabilized zirconia beads, 85% fill, 3,000 rpm, residence time 4–6 passes) reliably achieves a particle size distribution with d₉₀ < 5 µm and d₅₀ < 2 µm (laser diffraction, Malvern Mastersizer 3000, Fraunhofer approximation). Exceeding 6 passes elevates slurry temperature above 50 °C and can trigger crystal growth via Ostwald ripening if the ethylene oxide/propylene oxide block copolymer stabilizer (typically 2.5–4.0% w/w) is depleted by thermal oxidation.
Seed Piece Treatment on Potato: When Tuber-Borne Inoculum Dictates Loading Rates
For the suppression of Rhizoctonia solani AG-3 on potato, thifluzamide is applied as a flowable concentrate for seed piece treatment (FS) at a rate of 15–25 g a.i./100 kg tubers. Calibration of the treatment slurry requires factoring in the specific surface area of the tuber lot: Russet Burbank lots with a higher proportion of size B tubers (surface area-to-mass ratio ≈ 0.012 m²/kg) receive the upper bound of the rate range to maintain a minimum active ingredient deposit of 0.2 µg a.i./cm². Deposition thresholds were established through image-analysis-based fluorescence tracer studies using a backpack spray-tunnel fitted with a revolving roller table (18 RPM) and a single flat-fan nozzle delivering 2.0 L slurry/tonne. The critical failure mode on the seed piece treatment line is excessive suction-side shear in the diaphragm pump recirculation loop; recirculation times exceeding 20 minutes during batch mixing have been observed to increase viscosity of the FS formulation past 800 mPa·s (Brookfield RVDV-II+, spindle 3, 20 rpm, 20 °C), causing uneven coverage and clogging of the in-line 50-mesh screen filters. Adding 0.02% w/w xanthan gum as an anti-settling agent resolves overnight sedimentation but must be hydrated for a minimum of 90 minutes under moderate agitation to reach full yield stress development.
When compared to fludioxonil-based seed treatments, thifluzamide exhibits a distinct benefit profile against the root-pruning symptom of Rhizoctonia canker rather than only suppressing black scurf. In Washington State University trials (Othello, WA, 2020), 20 g a.i./100 kg thifluzamide reduced root galling severity by 41% relative to the untreated check, versus 18% for fludioxonil at 2.5 g a.i./100 kg, although black scurf index differences did not reach statistical significance. These results anchor the recommendation that thifluzamide should be integrated into a sequential program with a stolon-initiating-stage foliar SDHI, not as a standalone replacement for broad-spectrum contact chemistries.
Resistance Management Window and Cross-Resistance Risks
Target-site resistance to SDHI fungicides in R. solani is conferred principally by histidine-to-tyrosine substitutions at codon 257 (H257Y) or 132 (H132Y/R) of the succinate dehydrogenase subunit B (sdhB) gene. In vitro sensitivity screening of 137 AG-1 IA isolates from the Mississippi Delta (2018–2022) using a microtitre mycelial growth assay (YBA agar, 0, 0.01, 0.1, 1, 10, 50 µg/mL thifluzamide technical, 4-day incubation at 28 °C) determined a baseline EC₅₀ range of 0.06–0.32 µg/mL. Isolates carrying the H257Y allele displayed EC₅₀ values shifted to 1.2–3.8 µg/mL, a resistance factor of 10–20, indicating reduced sensitivity but not full practical resistance. Because thifluzamide binds within the same ubiquinone pocket as other SDHIs, cross-resistance with boscalid, penthiopyrad, and isopyrazam is positive; isolates showing high-level boscalid resistance (EC₅₀ > 50 µg/mL) typically retain only marginal sensitivity to thifluzamide. Commodity-specific FRAC guidelines (FRAC Code 7) mandate a maximum of 2 applications per season for thifluzamide-containing products in rice and 1 application per season on potato, with strict alternation to a non-SDHI mode of action such as a QoI (FRAC 11) or a phenylpyrrole (FRAC 12) for the intervening spray.
Comparative physicochemical properties of selected SDHI fungicides relevant to formulation and environmental fate
Property
Thifluzamide
Boscalid
Penthiopyrad
Isofetamid
Log P (25 °C, OECD 117)
4.1
2.9
4.6
3.5
Aqueous solubility (mg/L, 20 °C)
1.6
4.6
1.36
2.2
Hydrolysis DT₅₀ (pH 7, 40 °C)
>30 d
>30 d
>30 d
171 d
Soil photolysis DT₅₀ (summer sunlight)
8.5 d
19 d
11 d
No published data
SC suspensibility (CIPAC MT 184.1, %)
≥ 92
≥ 88
≥ 90
≥ 95
Combination of thifluzamide with organophosphate insecticides such as profenofos or chlorpyrifos in the same tank is discouraged without a jar test verified under the target water quality profile. Hydrolysis rates in the presence of 0.1 M phosphate buffer at pH 8.5—a pH range common in rice paddy water during algal blooms—increase by a factor of 1.7 when 500 mg/L of profenofos emulsifiable concentrate is co-introduced, likely due to surfactant-facilitated solubilization and base-catalysed cleavage of the amide linkage bridging the thiazole and anilide rings. Field observations from the Texas Rice Belt have recorded a 9–12% reduction in sheath blight suppression when the spray solution pH exceeded 8.2, a condition avoidable by pre-acidification with 0.01% v/v buffered phosphoric acid solution to a target pH of 6.0–6.5 before pesticide addition.
Seed treatment slurries incorporating thifluzamide FS must not be stored in carbon steel tanks beyond 4 hours; electrochemical testing (ASTM G31-21 immersion coupon, 1018 carbon steel, 72 hours, 25 °C) showed a corrosion rate of 0.15 mm/year, attributed to trace bromide release from the dibromo substituents under reductive conditions. This is a formulation stability parameter not commonly monitored with non-halogenated SDHI actives and necessitates 316L stainless steel or high-density polyethylene vessels in seed treatment plants.
Regulatory Classification Tier and Maximum Residue Limits
Toxicity classification per GHS Revision 9 places thifluzamide technical in Category 4 for acute oral toxicity (rat LD₅₀ > 5,000 mg/kg, OECD 423) and Category 2 for specific target organ toxicity—repeated exposure based on a NOAEL of 2.6 mg/kg bw/day from a 90-day rat feeding study (OECD 408). The compound exhibits no genotoxic potential (Ames test, OECD 471; in vivo micronucleus, OECD 474) and is not classified as a carcinogen under EPA guidelines (2005). Ecotoxicological endpoints drive label buffer zones: the 96-hour LC₅₀ for Oncorhynchus mykiss is 0.49 mg/L (OECD 203, flow-through), and the 48-hour EC₅₀ for Daphnia magna is 0.18 mg/L (OECD 202, static). Consequently, EU registration (Reg. (EC) No 1107/2009) imposes a 10-metre no-spray buffer for aerial application adjacent to surface water bodies.
Global MRL tolerances vary significantly by commodity and importing jurisdiction: the Codex MRL for rice is 1.5 mg/kg, while Japan enforces a stricter rice MRL of 0.7 mg/kg. Potato tubers carry a Codex MRL of 0.1 mg/kg, which aligns with EU Regulation 396/2005 Annex II. Analytical enforcement relies on QuEChERS extraction (EN 15662:2018) followed by LC-MS/MS determination, with a limit of quantification of 0.01 mg/kg for all substrates.
Manufacturing supply chains shipping technical material into the EU must accompany each batch with certificates demonstrating compliance with REACH Annex XVII restrictions and sub-0.1% w/w content of any substance listed on the Candidate List of SVHCs. Persistent stock of thifluzamide SC stored under tropical warehouse conditions (ambient > 35 °C, > 75% RH) for periods exceeding 18 months has, in isolated incidents at a central Java storage hub, developed crystal growth and sedimentation irreversible by normal recirculation; accelerated storage stability testing per CIPAC MT 46.3 at 54 °C for 14 days is predictive of this failure mode and should be included in batch release criteria with an acceptance threshold of ≤ 2% increase in d₉₀ particle size.