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205650-65-3

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  • 5-AMINO-1-[2,6-DIFLUORO-4-(TRIFLUOROMETHYL) PHENY L]-1H PYRAZOLE-3-CARBONITRILE Pyrazol derivatives CAS NO.205650-65-3

    Cas No: 205650-65-3

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205650-65-3 Usage

Uses

Fipronil Desulfinyl is a photodegradation product of Fipronil (F342200).

Check Digit Verification of cas no

The CAS Registry Mumber 205650-65-3 includes 9 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 6 digits, 2,0,5,6,5 and 0 respectively; the second part has 2 digits, 6 and 5 respectively.
Calculate Digit Verification of CAS Registry Number 205650-65:
(8*2)+(7*0)+(6*5)+(5*6)+(4*5)+(3*0)+(2*6)+(1*5)=113
113 % 10 = 3
So 205650-65-3 is a valid CAS Registry Number.

205650-65-3SDS

SAFETY DATA SHEETS

According to Globally Harmonized System of Classification and Labelling of Chemicals (GHS) - Sixth revised edition

Version: 1.0

Creation Date: Aug 12, 2017

Revision Date: Aug 12, 2017

1.Identification

1.1 GHS Product identifier

Product name 5-amino-1-[2,6-dichloro-4-(trifluoromethyl)phenyl]-4-(trifluoromethyl)pyrazole-3-carbonitrile

1.2 Other means of identification

Product number -
Other names desulfinyl fipronil

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only.
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
Service hours Monday to Friday, 9am-5pm (Standard time zone: UTC/GMT +8 hours).

More Details:205650-65-3 SDS

205650-65-3Upstream product

205650-65-3Downstream Products

205650-65-3Relevant articles and documents

Chiral resolution of the insecticide fipronil enantiomers and the simultaneous determination of its major transformation products by high-performance liquid chromatography interfaced with mass spectrometry

Paolini, Léa,Hausser, Nicolas,Zhang, Tong

supporting information, p. 473 - 483 (2022/01/22)

A high-performance liquid chromatography–mass spectrometry (HPLC-MS) method was developed using a chiral column based on amylose tris(3-chloro-5-methylphenylcarbamate) for analysis of fipronil (a popular insecticidal nerve agent) and the related transformation products. The optimized method reached the goal of the simultaneous and complete separation of the multiple fiproles in a single run, including the chiral separation of fipronil enantiomers, fipronil metabolites, and photoproducts. The efficacy of such a method was demonstrated by its application in analyzing a series of fipronil samples exposed to sunlight conditions. In general terms, our study provided experimental approaches and an efficient analytical tool for monitoring the environmental fate of fipronil as well as its multitransformation products upon its applications either in agricultural or any other areas.

Kinetics and Mechanisms of Abiotic Degradation of Fipronil (Hydrolysis and Photolysis)

Bobe, Alain,Meallier, Pierre,Cooper, Jean-Francois,Coste, Camille M.

, p. 2834 - 2839 (2007/10/03)

The abiotic degradation of fipronil (compound I), a phenylpyrazole insecticide, was studied in aqueous solution and on the surface of two soils from Niger (Saguia and Banizoumbou) and one Mediterranean soil (Montpellier). The rate of hydrolysis of fipronil in solution was measured at different values of pH and temperature. The pH was an influencing factor: hydrolysis kinetics were pseudo-firstorder, the half-life being 770 h at pH 9.0, 114 h at pH 10.0, 11 h at pH 11.0, and 2.4 h at pH 12.0. Fipronil was stable under acid (pH 5.5) and neutral conditions. The Arrhenius relation was verified over the temperature range 22-45 °C: the activation energy was 62 kJ mol-1 and the calculated entropy change -32 J mol-1. Compound II [5-amino-3-carbamoyl-1-(2,6-dichloro-4-(trifluoromethyl)-phenyl)-4- [(trifluoromethyl)sulfinyl]pyrazole] was the only hydrolysis product detected. The hydrolysis reaction mechanism involves nucleophilic addition of OH- to the polar nitrile bond, producing a hydroxyimine which then undergoes tautomerization into an amide. Fipronil in acidic (pH 5.5) aqueous solution exposed to light from a xenon lamp degraded with first-order kinetics (Kobs, = 1.7 h-1) with concomitant appearance of 5-amino-3-cyano-1-(2,6-dichloro-4-(trifluoromethyl)phenyl)-4-(trifluoromethyl) pyrazole (compound III) and 5-amino-3-cyano-1-(2,6-dichloro-4-(trifluoromethyl)-phenyl)pyrazole-4-sulfonic acid (compound IV). The photolyte formation rate constants were 0.11 h-1 (III) and 0.05 h-1 (IV). The observed degradation process corresponded to a desulfinylation and an oxidation. The reaction mechanisms were not elucidated. The irradiation (xenon lamp) of fipronil adsorbed on three natural soils when dry led to the formation of 4-(trifluoromethyl)pyrazole (III). The Kobs values were 0.0047 h-1 (Saguia), 0.0039 h-1 (Banizoumbou), and 0.0032 h-1 (Montpellier). The degree of photodegradation was inversely proportional to fipronil adsorption: the Freundlich adsorption coefficients were, respectively, 4.3 (Saguia), 7.3 (Banizoumbou), and 45.5 (Montpellier).

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