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Merck

45883

Supelco

Metolachlor solution

100 μg/mL in acetonitrile, PESTANAL®, analytical standard

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About This Item

Fórmula empírica (notación de Hill):
C15H22ClNO2
Número de CAS:
Peso molecular:
283.79
Beilstein:
8396147
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

concentración

100 μg/mL in acetonitrile

técnicas

HPLC: suitable
gas chromatography (GC): suitable

aplicaciones

agriculture
environmental

Formato

single component solution

temp. de almacenamiento

2-8°C

cadena SMILES

CCc1cccc(C)c1N(C(C)COC)C(=O)CCl

InChI

1S/C15H22ClNO2/c1-5-13-8-6-7-11(2)15(13)17(14(18)9-16)12(3)10-19-4/h6-8,12H,5,9-10H2,1-4H3

Clave InChI

WVQBLGZPHOPPFO-UHFFFAOYSA-N

Categorías relacionadas

Aplicación

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

Información legal

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

Pictogramas

FlameExclamation mark

Palabra de señalización

Danger

Clasificaciones de peligro

Acute Tox. 4 Dermal - Acute Tox. 4 Inhalation - Acute Tox. 4 Oral - Eye Irrit. 2 - Flam. Liq. 2

Código de clase de almacenamiento

3 - Flammable liquids

Clase de riesgo para el agua (WGK)

WGK 2

Punto de inflamabilidad (°F)

35.6 °F - closed cup

Punto de inflamabilidad (°C)

2 °C - closed cup

Equipo de protección personal

Eyeshields, Faceshields, Gloves, type ABEK (EN14387) respirator filter


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Certificados de análisis (COA)

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Visite la Librería de documentos

J Restivo et al.
Journal of hazardous materials, 239-240, 249-256 (2012-09-27)
The catalytic ozonation of the herbicide metolachlor (MTLC) was tested using carbon nanomaterials as catalysts. Multiwalled carbon nanotubes were used in semi-batch experiments and carbon nanofibres grown on a honeycomb cordierite monolith were tested in continuous experiments. The application of
M T Moore et al.
Bulletin of environmental contamination and toxicology, 89(2), 292-295 (2012-06-02)
Phytotoxicity assessments were performed to compare responses of Typha latifolia (L.) seeds to atrazine (only) and atrazine + S-metolachlor exposure concentrations of 0.03, 0.3, 3, and 30 mg L(-1), as well as permethrin exposure concentrations of 0.008, 0.08, 0.8, and
Zisis Vryzas et al.
Chemosphere, 89(11), 1330-1338 (2012-06-29)
Biotransformation studies of atrazine, metolachlor and evolution of their metabolites were carried out in soils and subsoils of Northern Greece. Trace atrazine, its metabolites and metolachlor residues were detected in field soil samples 1 year after their application. The biotransformation
Huijun Liu et al.
Journal of hazardous materials, 217-218, 330-337 (2012-04-10)
Rac-metolachlor, a widely used chloracetanilide herbicide, is now being replaced by S-metolachlor in many countries. The enantioselective effects of rac- and S-metolachlor on root growth of maize and rice was studied in hydroponics. Visible morphological changes in root growth were
Yongnian Ni et al.
Spectrochimica acta. Part A, Molecular and biomolecular spectroscopy, 97, 753-761 (2012-08-18)
Enantioselective binding interaction of the pesticides, metolachlor (RAC-metolachlor) and its S-enantiomer (S-metolachlor), with bovine serum albumin (BSA) was investigated by fluorescence and UV-vis absorption spectroscopy. Both RAC- and S-metolachlors quenched the intrinsic fluorescence of BSA via a static mechanism, and

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