144740-59-0 Usage
Description
Methyl 2-aminosulfonyl-6-(trifluoromethyl)pyridine-3-carboxylate is a chemical compound with a unique molecular structure that features a pyridine ring, a trifluoromethyl group, and a sulfonyl group. methyl 2-aminosulfonyl-6-(trifluoromethyl)pyridine-3-c arboxylate is characterized by its potential applications in various industries, particularly in agriculture.
Uses
Used in Agricultural Industry:
Methyl 2-aminosulfonyl-6-(trifluoromethyl)pyridine-3-carboxylate is used as a herbicidal agent for the soil of winter wheat crops. It helps in controlling the growth of unwanted plants and weeds, ensuring a healthy and productive crop yield. The compound's specific properties allow it to target and inhibit essential processes in the growth of weeds, thus providing an effective solution for weed management in winter wheat cultivation.
Check Digit Verification of cas no
The CAS Registry Mumber 144740-59-0 includes 9 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 6 digits, 1,4,4,7,4 and 0 respectively; the second part has 2 digits, 5 and 9 respectively.
Calculate Digit Verification of CAS Registry Number 144740-59:
(8*1)+(7*4)+(6*4)+(5*7)+(4*4)+(3*0)+(2*5)+(1*9)=130
130 % 10 = 0
So 144740-59-0 is a valid CAS Registry Number.
InChI:InChI=1/C8H7F3N2O4S/c1-17-7(14)4-2-3-5(8(9,10)11)13-6(4)18(12,15)16/h2-3H,1H3,(H2,12,15,16)
144740-59-0Relevant articles and documents
Fate and behaviour of flupyrsulfuron-methyl in soil and aquatic systems
Singles,Dean,Kirkpatrick,Mayo,Langford-Pollard,Barefoot,Bramble F.Q.
, p. 288 - 300 (2007/10/03)
The environmental fate of [14C] flupyrsulfuron-methyl, a sulfonylurea herbicide, was investigated in soil and aquatic systems. The major degradative pathways in both systems were contraction of the sulfonylurea bridge followed by intramolecular rearrangement (at pH > 7) or sulfonylurea bridge hydrolysis (at pH 50 3-6 days), degradation being faster in the aerobic aquatic systems than in sterile buffers. Degradation in aerobic soils was rapid, both in the laboratory (DT50 8-26 days) and in the field (DT50 6- 11 days, DT90 35-123 days). In laboratory studies the rate of degradation in soil reduced with decreasing temperature (rate at 10°C half that at 20°C) but was unaffected by soil water content (50% vs 70% maximum water holding capacity). The compound was degraded in flooded anaerobic soils (DT50 33 days). Flupyrsulfuron-methyl was weakly absorbed to soils, there being a linear relationship between adsorption and soil organic carbon content. Following application of [14C]flupyrsulfuron-methyl to bare field soil the radioactivity moved little, with very little radioactivity found in soil below 60 cm from the surface.
