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Supelco

Metolachlor solution

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

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About This Item

Fórmula empírica (Notação de Hill):
C15H22ClNO2
Número CAS:
51218-45-2
Peso molecular:
283.79
Beilstein:
8396147
Número CE:
200-835-2
Número MDL:
MFCD00055293
Código UNSPSC:
41116107
ID de substância PubChem:
329757000
NACRES:
NA.24

grau

analytical standard

Nível de qualidade

100

linha de produto

PESTANAL®

prazo de validade

limited shelf life, expiry date on the label

concentração

100 μg/mL in acetonitrile

técnica(s)

HPLC: suitable
gas chromatography (GC): suitable

aplicação(ões)

agriculture
environmental

formato

single component solution

temperatura de armazenamento

2-8°C

cadeia de caracteres 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

chave InChI

WVQBLGZPHOPPFO-UHFFFAOYSA-N

Categorias relacionadas

Aplicação

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

Informações legais

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

Pictogramas

FlameExclamation mark
GHS02,GHS07

Palavra indicadora

Danger

Classificações de perigo

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

Código de classe de armazenamento

3 - Flammable liquids

Classe de risco de água (WGK)

WGK 2

Ponto de fulgor (°F)

35.6 °F - closed cup

Ponto de fulgor (°C)

2 °C - closed cup

Equipamento de proteção individual

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

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Certificados de análise (COA)

Lot/Batch Number
BCCM3533
BCCD1604
BCBS4755V
SZBE062XV
SZBD227XV

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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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