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45400

Supelco

Chlortoluron

PESTANAL®, analytical standard

Synonym(s):

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

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About This Item

Empirical Formula (Hill Notation):
C10H13ClN2O
CAS Number:
15545-48-9
Molecular Weight:
212.68
Beilstein:
2647688
EC Number:
239-592-2
MDL number:
MFCD00018275
UNSPSC Code:
41116107
PubChem Substance ID:
329756703
NACRES:
NA.24

grade

analytical standard

Quality Level

100

product line

PESTANAL®

shelf life

limited shelf life, expiry date on the label

technique(s)

HPLC: suitable
gas chromatography (GC): suitable

application(s)

agriculture
cleaning products
cosmetics
environmental
food and beverages
personal care

format

neat

SMILES string

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)

InChI key

JXCGFZXSOMJFOA-UHFFFAOYSA-N

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Application

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

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Legal Information

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

Pictograms

Health hazardEnvironment
GHS08,GHS09

Signal Word

Warning

Hazard Statements

H351,H361fd,H410

Hazard Classifications

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

Storage Class Code

11 - Combustible Solids

WGK

WGK 3

Flash Point(F)

Not applicable

Flash Point(C)

Not applicable

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Certificates of Analysis (COA)

Lot/Batch Number
BCCJ4901
BCCH5435
BCBW1414
SZBD238XV
SZBA218XV

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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
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.
J Villaverde et al.
Environmental science & technology, 43(21), 8227-8232 (2009-11-21)
This study investigates time-dependent sorption of pesticides in soil aggregates. We tested if the sorption kinetics of pesticides in soil aggregates can be described by modeling diffusion into aggregates for a range of soils and pesticides. Our hypothesis is that
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
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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