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46277

Supelco

Esfenvalerate

PESTANAL®, analytical standard

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About This Item

Fórmula empírica (Notação de Hill):
C25H22ClNO3
Número CAS:
Peso molecular:
419.90
Beilstein:
4275674
Número MDL:
Código UNSPSC:
41116107
ID de substância PubChem:
NACRES:
NA.24

grau

analytical standard

Nível de qualidade

linha de produto

PESTANAL®

prazo de validade

limited shelf life, expiry date on the label

técnica(s)

HPLC: suitable
gas chromatography (GC): suitable

aplicação(ões)

agriculture
environmental

Formato

neat

cadeia de caracteres SMILES

CC(C)[C@H](C(=O)O[C@H](C#N)c1cccc(Oc2ccccc2)c1)c3ccc(Cl)cc3

InChI

1S/C25H22ClNO3/c1-17(2)24(18-11-13-20(26)14-12-18)25(28)30-23(16-27)19-7-6-10-22(15-19)29-21-8-4-3-5-9-21/h3-15,17,23-24H,1-2H3/t23-,24+/m1/s1

chave InChI

NYPJDWWKZLNGGM-RPWUZVMVSA-N

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Aplicação

Esfenvalerate may be used as an analytical reference standard for the quantification of the analyte in environmental samples using gas chromatography-negative ion chemical ionization mass spectrometry (GC-NCI-MS).
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

Palavra indicadora

Danger

Classificações de perigo

Acute Tox. 3 Inhalation - Acute Tox. 3 Oral - Aquatic Acute 1 - Aquatic Chronic 1 - Skin Sens. 1 - STOT RE 2 - STOT SE 1

Órgãos-alvo

Nervous system

Código de classe de armazenamento

6.1C - Combustible acute toxic Cat.3 / toxic compounds or compounds which causing chronic effects

Classe de risco de água (WGK)

WGK 3

Ponto de fulgor (°F)

Not applicable

Ponto de fulgor (°C)

Not applicable

Equipamento de proteção individual

Eyeshields, Faceshields, Gloves, type P2 (EN 143) respirator cartridges


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Nedim Tüzün et al.
Environmental science & technology, 51(23), 13949-13956 (2017-11-08)
Current ecological risk assessment of pesticides fails to protect aquatic biodiversity. For the first time, we tested two potential reasons for this failure with regard to carry-over effects across metamorphosis: their dependence on hatching period, and the lack of studies
Mark G Teese et al.
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John L Maron et al.
Ecology, 99(2), 464-473 (2017-12-06)
Many clonal organisms occasionally outcross, but the long-term consequences of such infrequent events are often unknown. During five years, representing three to five plant generations, we followed 16 experimental field populations of the forb, Oenothera biennis, originally planted with the same
Matthias Liess et al.
Scientific reports, 9(1), 15248-15248 (2019-10-28)
We present a model to identify the effects of low toxicant concentrations. Due to inadequate models, such effects have so far often been misinterpreted as random variability. Instead, a tri-phasic relationship describes the effects of a toxicant when a broad
Warren Kunce et al.
Aquatic toxicology (Amsterdam, Netherlands), 190, 70-77 (2017-07-12)
Direct mortality due to toxicity of single pesticide exposure along a concentration gradient, while the most common, is only one important parameter for assessing the effects of pesticide contamination on aquatic ecosystems. Sub-lethal toxicity can induce changes in an organism's

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