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Supelco

Metolachlor solution

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

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About This Item

Formule empirique (notation de Hill):
C15H22ClNO2
Numéro CAS:
Poids moléculaire :
283.79
Numéro Beilstein :
8396147
Numéro CE :
Numéro MDL:
Code UNSPSC :
41116107
ID de substance PubChem :
Nomenclature NACRES :
NA.24

Qualité

analytical standard

Niveau de qualité

Gamme de produits

PESTANAL®

Durée de conservation

limited shelf life, expiry date on the label

Concentration

100 μg/mL in acetonitrile

Technique(s)

HPLC: suitable
gas chromatography (GC): suitable

Application(s)

agriculture
environmental

Format

single component solution

Température de stockage

2-8°C

Chaîne 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

Clé InChI

WVQBLGZPHOPPFO-UHFFFAOYSA-N

Catégories apparentées

Application

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

Informations légales

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

Pictogrammes

FlameExclamation mark

Mention d'avertissement

Danger

Classification des risques

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

Code de la classe de stockage

3 - Flammable liquids

Classe de danger pour l'eau (WGK)

WGK 2

Point d'éclair (°F)

35.6 °F - closed cup

Point d'éclair (°C)

2 °C - closed cup

Équipement de protection individuelle

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


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Certificats d'analyse (COA)

Lot/Batch Number

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Retrouvez la documentation relative aux produits que vous avez récemment achetés dans la Bibliothèque de documents.

Consulter la Bibliothèque de documents

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
Huong Mai et al.
Marine pollution bulletin, 64(12), 2663-2670 (2012-11-06)
This study evaluated embryotoxicity and genotoxicity of two dissolved metals copper and cadmium (Cu and Cd) and two pesticides (metolachlor and irgarol) occurring in Arcachon Bay (SW France) in Pacific oyster (Crassostrea gigas) larvae and investigated the relationship between those
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
Megha Thakkar et al.
Aquatic toxicology (Amsterdam, Netherlands), 126, 198-206 (2012-12-12)
Metolachlor, a chloroacetanilide herbicide, has been frequently detected in coastal waters. This study examined the growth, photosynthesis, and detoxification responses of chlorophyte Dunaliella tertiolecta (DT) and brown tide alga Aureococcus anophagefferens (AA) upon 5-day exposure to 0.5-5 mg L(-1) metolachlor.

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