NICOSULFURON
Herbicide
HRAC B WSSA 2; sulfonylurea |
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NOMENCLATURE
Common name nicosulfuron (BSI, ANSI, draft E-ISO);
no name (Brazil)
IUPAC name 2-(4,6-dimethoxypyrimidin-2-ylcarbamoylsulfamoyl)-N,N-dimethylnicotinamide;
1-(4,6-dimethoxypyrimidin-2-yl)-3-(3-dimethylcarbamoyl-2-pyridylsulfonyl)urea
Chemical Abstracts name 2-[[[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]amino]sulfonyl]-N,N-dimethyl-3-pyridinecarboxamide
CAS RN [111991-09-4]
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PHYSICAL
CHEMISTRY
Mol. wt. 410.4 M.f. C15H18N6O6S Form Colourless crystals. M.p. 169-172 ˇăC V.p. <8 ´ 10-7 mPa (25 ˇăC) KOW logP = -0.36 (pH 5), -1.8 (pH 7), -2 (pH 9)
Henry <4.68 ´ 10-9 Pa m3 mol-1 (25 ˇăC) S.g./density 0.313 (bulk)
Solubility In water 0.07 g/l. In acetone 18, ethanol 4.5, chloroform, dimethylformamide
64, acetonitrile 23, toluene 0.370, hexane <0.02,
dichloromethane 160 (all in g/kg, 25 ºC).
Stability Hydrolysis DT50 15 d (pH 5);
stable at pH 7 & 9.
pKa 4.6 (25 ºC) F.p. >200 ˇăC (Cleveland open cup) |
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APPLICATIONS
Biochemistry Branched chain
amino acid synthesis (ALS or AHAS) inhibitor.
Acts by inhibiting biosynthesis of the essential
amino acids valine and isoleucine, hence stopping
cell division and plant growth. Maize selectivity
derives from selective metabolism (P450-mediated
pyrimidine-5-hydroxylation, followed by conjugation
with glucose).
Mode of action Selective systemic herbicide, absorbed by the
foliage and roots, with rapid translocation
in xylem and phloem to the meristematic tissues.
Uses Selective post-emergence control in maize of annual grass weeds including
Setaria, Echinochloa, Digitaria, Panicum, Lolium, and Avena spp., broad-leaved weeds including Amaranthus spp. and Cruciferae, and perennials such as
Sorghum halepense and Agropyron repens. Applied at 35-70 g/ha. Formulation types SC; WG. |
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| ANALYSIS
Product by hplc.
Methods for sulfonylurea residues in
crops, soil and water reviewed (A. C. Barefoot
et al., Proc. Br. Crop Prot. Conf. - Weeds,
1995, 2, 707). Details from Ishihara
Sangyo. |
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MAMMALIAN
TOXICOLOGY
Reviews Material Safety Data Sheets (available
from Du Pont).
Oral Acute oral LD50 for male and
female rats and mice >5000 mg/kg.
Skin and eye Acute percutaneous LD50 for male and female rats >2000 mg/kg. Moderate
eye irritant; not a skin irritant (rabbits);
not a skin sensitiser (guinea pigs). The 75%
formulation is not an eye irritant. Inhalation LC50 for rats (4 h) 5.47 mg/l. NOEL In 28 d feeding trials on rats and mice, no adverse effect up to 30 g/kg
diet.
Other Non-mutagenic in the Ames test. Toxicity class WHO (a.i.) III (Table 5); EPA (formulation)
IV |
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ECOTOXICOLOGY
Birds Dietary oral LD50 for bobwhite quail >2250 mg/kg. Dietary
LC50 for mallard ducks and bobwhite quail
>5620 ppm.
Fish LC50 (96 h) for bluegill sunfish and rainbow
trout >1000 mg/l.
Daphnia LC50 (48 h) >1000 mg/l. Algae NOEC (96 h) for green algae 100 mg/l. Bees LD50 (contact) >20 mg/bee; dietary LC50 (48 h) >1000 ppm. NOEC 500 ppm. Worms LC50 (14 d) for earthworms >1000 mg/kg.
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ENVIRONMENTAL
FATE
Animals In goats, following a dose of 60 ppm, <0.1
ppm was found in tissues and milk; therefore
nicosulfuron and its metabolites do not bioaccumulate.
Hydrolysis of the sulfonylurea bridge and hydroxylation
were the main metabolic pathways.
Plants Degraded rapidly in maize, DT50 1.5-4.5 d. Residues <0.02 ppm in all crops.
Hydrolysis of the sulfonylurea bridge to form
the pyridine sulfonamide and pyrimidine amine,
and hydroxylation on the pyrimidine ring, were
the main metabolic pathways.
Soil/Environment Soil DT50 (aerobic) 26 d (pH 6.1, 5.1% o.m., 25 ˇăC).
In four sandy loams, Kd (25 ˇăC) 0.16
(pH 6.6, 1.1% o.m.) to 1.73 (pH 5.4, 4.3% o.m.).
Photolysis DT50 (soil) 60-67 d; (water) 14-19 d (pH 5), 200-250
d (pH 7), 180-200 d (pH 9). Values from separate
studies were: Soil DT50 24-43 d (20 ˇăC); DT90 80-143 d (20 ˇăC). Kd 0.05-0.7. In water, DT50 15 d (pH 5, 20 ˇăC). |
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