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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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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.
Malik M Haque et al.
Environmental science & technology, 40(15), 4765-4770 (2006-08-18)
The photocatalytic degradation of a herbicide derivative, chlorotoluron [3-(3-chloro-4-methylphenyl)-1,1-dimethylurea, 1], has been investigated in aqueous suspensions of titanium dioxide (TiO2) under a variety of conditions. The degradation was studied by monitoring the change in substrate concentration employing UV spectroscopic analysis
Sylvie Nélieu et al.
Environmental toxicology and chemistry, 29(12), 2644-2652 (2010-10-12)
The ecotoxicological impact of nitrate-induced photodegradation products of diuron and chlorotoluron was studied through monospecific biotests conducted in conjunction with experiments in outdoor aquatic mesocosms. Organisms representing three trophic levels were used: two heterotrophic microorganisms, the luminescent bacterium Vibrio fischeri
Robin G Oliver et al.
Pest management science, 69(1), 120-125 (2012-08-29)
It is important to understand the degradation of organic molecules in surface waters to ensure that risk assessments, intended to prevent adverse effects on human health and the environment, are robust. One important degradation mechanism in surface waters is photodegradation.
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
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