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Merck

45400

Supelco

Chlortoluron

PESTANAL®, analytical standard

Sinónimos:

3-(3-Chloro-4-methyl)-1,1-dimethylurea

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About This Item

Fórmula empírica (notación de Hill):
C10H13ClN2O
Número de CAS:
Peso molecular:
212.68
Beilstein:
2647688
Número CE:
Número MDL:
Código UNSPSC:
41116107
ID de la sustancia en PubChem:
NACRES:
NA.24

grado

analytical standard

Nivel de calidad

Línea del producto

PESTANAL®

caducidad

limited shelf life, expiry date on the label

técnicas

HPLC: suitable
gas chromatography (GC): suitable

aplicaciones

agriculture
cleaning products
cosmetics
environmental
food and beverages
personal care

formato

neat

cadena SMILES

CN(C)C(=O)Nc1ccc(C)c(Cl)c1

InChI

1S/C10H13ClN2O/c1-7-4-5-8(6-9(7)11)12-10(14)13(2)3/h4-6H,1-3H3,(H,12,14)

Clave InChI

JXCGFZXSOMJFOA-UHFFFAOYSA-N

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Aplicación

Refer to the product′s Certificate of Analysis for more information on a suitable instrument technique. Contact Technical Service for further support.

Productos recomendados

Find a digital Reference Material for this product available on our online platform ChemisTwin® for NMR. You can use this digital equivalent on ChemisTwin® for your sample identity confirmation and compound quantification (with digital external standard). An NMR spectrum of this substance can be viewed and an online comparison against your sample can be performed with a few mouseclicks. Learn more here and start your free trial.

Información legal

PESTANAL is a registered trademark of Merck KGaA, Darmstadt, Germany

Pictogramas

Health hazardEnvironment

Palabra de señalización

Warning

Frases de peligro

Clasificaciones de peligro

Aquatic Acute 1 - Aquatic Chronic 1 - Carc. 2 - Repr. 2

Código de clase de almacenamiento

11 - Combustible Solids

Clase de riesgo para el agua (WGK)

WGK 3

Punto de inflamabilidad (°F)

Not applicable

Punto de inflamabilidad (°C)

Not applicable


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Yaron Drori et al.
Journal of environmental quality, 35(6), 2154-2161 (2006-10-31)
The soil lipid fraction can play an important role in the sorption of organic compounds. In this study, the impact of the lipid fraction of freshwater- and wastewater-irrigated soils on the sorption of non- and relatively polar compounds was assessed.
Min-Ling Gao et al.
Journal of environmental sciences (China), 19(3), 327-331 (2007-10-09)
Sorption of chlorotoluron in ammonium sulfate, urea and atrazine multi-solutes system was investigated by batch experiments. The results showed application of nitrogen fertilizers to the soil could affect the behavior of chlorotoluron. At the same concentration of N, sorption of
Bin Xu et al.
The Science of the total environment, 417-418, 241-247 (2012-01-26)
The degradation of chlortoluron by monochloramination was investigated in the pH range of 4-9. The degradation kinetics can be well described by a second-order kinetic model, first-order in monochloramine (NH(2)Cl) and first-order in chlortoluron. NH(2)Cl was found not to be
Sylvie Nélieu et al.
Environmental science & technology, 43(9), 3148-3154 (2009-06-19)
The nitrate-induced photodegradation of chlorotoluron was demonstrated to occur efficiently in natural water through two series of experiments in outdoor aquatic mesocosms. During the first campaign, it was shown that the pesticide degradation kinetics was clearly dependent on nitrate concentration.
Claire Valiente Moro et al.
Environmental toxicology and chemistry, 31(4), 778-786 (2012-01-27)
Extensive use of herbicides in agriculture is accompanied by the risk of environmental contamination of aquatic ecosystems. The present study shows the effects of the herbicides chlortoluron and mesotrione on three microalgae species: two chlorophyceae (Pediastrum tetras, Ankistrodesmus fusiformis) and

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