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Cyazofamid

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Common name cyazofamid (BSI, E-ISO); cyazofamide ((m) F-ISO)


 
IUPAC name 4-chloro-2-cyano-N,N-dimethyl-5-p-tolylimidazole-1-sulfonamide
Chemical Abstracts name 4-chloro-2-cyano-N,N-dimethyl-5-(4-methylphenyl)-1H-imidazole-1-sulfonamide CAS RN [120116–88–3] Development codes IKF-916 (Ishihara Sangyo) Smiles code CN(C)S(=O)(=O)n1c(C#N)nc(Cl)c1c2ccc(C)cc2
 
 
Composition Tech is ≥93.5% pure.
 
Mol. wt. 324.8 M.f. C13H13ClN4O2S Form Ivory, odourless powder. M.p. 152.7 °C V.p. <1.3 × 10-2 mPa (35 °C) Kow logP = 3.2 (25 °C) Henry <4.03 × 10-2 Pa m3 mol-1 (20 °C, calc.) S.g./density 1.446 (20 °C) Solubility In water 0.121 (pH 5), 0.107 (pH 7), 0.109 (pH 9) (all in ppm, 20 °C). In acetone 41.9, toluene 5.3, dichloromethane 101.8, hexane 0.03, ethanol 1.54, ethyl acetate 15.63, octanol 0.25, acetonitrile 29.4, isopropanol 0.39 (all in g/l, 20 °C). Stability In water DT50 24.6 d (pH 4), 27.2 d (pH 5), 24.8 d (pH 7).
 
 
Biochemistry ‘Quinone inside Inhibitor’. Both cyazofamid and the strobilurin fungicides inhibit at complex III (ubiquinol-cytochrome c reductase) in the mitochondrial respiratory chain. However, cyazofamid inhibits Qi (the ubiquinone reducing site) of cytochrome bc1, whereas the strobilurins inhibit Qo (the ubiquinol oxidising site) of cytochrome bc1. Selectivity appears to be due to a difference in the susceptibility of the target enzyme. Mode of action Foliar and soil preventive fungicide with residual activity and rainfastness, together with moderate translaminar and curative activity. Inhibits all stages in the lifecycle of Phytophthora infestans.
 
Uses For control of Oomycete and Plasmodiophora diseases, such as potato and tomato late blight (Phytophthora infestans) and downy mildews (e.g. Pseudoperonospora cubensis of cucumber), at 60–100 g/ha. Its use as a foliar treatment on other crops, such as vines, onions, lettuce, rice and crucifers, is under investigation.
 
 
 
EU Rev. Rep. SANCO/10379/2002, Nov. 2002. EPA Fact Sheet, Sep. 2004. FSC Eval. Rep., 2004. 91/414/EC Annex I status Included, 2003/23/EC.
 
 
Oral Acute oral LD50 for rats and mice >5000 mg/kg. Skin and eye Acute percutaneous LD50 for rats >2000 mg/kg. Not irritating to eyes or skin (rabbits). Not a skin sensitiser (guinea pigs). Inhalation LC50 for rats >5.5 mg/l. NOEL NOAEL for male rats 500 ppm (17 mg/kg b.w. daily). ADI/RfD (EC) 0.17 mg/kg b.w. [2003]; (EPA) aRfD 1.0, cRfD 0.95 mg/kg b.w. [2004]; (FSC) 0.17 mg/kg b.w. [2004] Other Negative in Ames, REC assay, chromosomal aberration and mouse micronucleus tests.
 
 
Birds Acute oral LD50 for quail and ducks >2000 mg/kg. Dietary LC50 for quail and ducks >5000 ppm (EU Rev. Rep.). Fish LC50 (96 h) for rainbow trout >0.510, carp >0.14 mg/l (both the highest achievable concentration in water). Daphnia EC50 (48 h) >0.14 mg/l (highest achievable concentration in water). Algae EbC50 (72 h) for Selenastrum capricornutum 0.025 mg/l. Bees LD50 for honeybees (oral) >151.7 μg/bee; (contact) >100 μg/bee. Worms Acute LC50 (14 d) for earthworms >1000 mg/kg. Other beneficial spp. Harmless to Aphidius rhopalosiphi, Typhlodromus pyri, Chrysoperla carnea and Aleochara bilineata (IOBC).
 
 
Animals Rapidly absorbed, with 90% excreted within 24 h in faeces and in urine. Excreted material was mainly unchanged cyazofamid and 4-(4-chloro-2-cyanoimidazol-5-yl)benzoic acid (EU Rev. Rep., EPA Fact Sheet, FSC Eval. Rep.). Plants Cyazofamid is poorly absorbed from soil or foliar application (tomatoes). The main residue component is unchanged parent. (FSC Eval. Rep.). Soil/Environment Rapidly degraded in soil, DT50 3–5 d; the main end metabolite is 4-chloro-5-p-tolylimidazole-2-carboxylic acid. DT50 for aerobic aquatic metabolism c. 10–18 d; 4-chloro-5-p-tolylimidazole-2-carbonitrile is the major degradate. Soil Koc 736–2172 (EPA Fact Sheet).