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45814

Supelco

Iprobenfos

PESTANAL®, analytical standard

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About This Item

Empirical Formula (Hill Notation):
C13H21O3PS
CAS Number:
Molecular Weight:
288.34
Beilstein:
1974687
EC Number:
MDL number:
UNSPSC Code:
41116107
PubChem Substance ID:
NACRES:
NA.24

grade

analytical standard

Quality Level

product line

PESTANAL®

shelf life

limited shelf life, expiry date on the label

technique(s)

HPLC: suitable
gas chromatography (GC): suitable

application(s)

agriculture
environmental

format

neat

storage temp.

2-8°C

SMILES string

CC(C)OP(=O)(OC(C)C)SCc1ccccc1

InChI

1S/C13H21O3PS/c1-11(2)15-17(14,16-12(3)4)18-10-13-8-6-5-7-9-13/h5-9,11-12H,10H2,1-4H3

InChI key

FCOAHACKGGIURQ-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.

Legal Information

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

Pictograms

Exclamation markEnvironment

Signal Word

Warning

Hazard Statements

Hazard Classifications

Acute Tox. 4 Oral - Aquatic Chronic 2

Storage Class Code

10 - Combustible liquids

WGK

WGK 2

Flash Point(F)

Not applicable

Flash Point(C)

Not applicable

Personal Protective Equipment

dust mask type N95 (US), Eyeshields, Gloves

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Certificates of Analysis (COA)

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Jee-Hyun Jung et al.
Marine environmental research, 63(5), 471-478 (2007-02-16)
Cholinesterases (ChEs) have been characterized in marbled sole (Limanda yokohamae) for use as a possible biomarker of pollution exposure. In brain, ChEs existed almost exclusively (>95%) as acetylcholinesterase (AChE) whereas in muscle, about 20-30% of ChE activity was in the
[Comparative study of the effect of the monotonous and intermittent action of ricid II on the bodies of animals].
L V Ruza
Gigiena i sanitariia, (11)(11), 77-79 (1986-11-01)
Seonock Woo et al.
Comparative biochemistry and physiology. Toxicology & pharmacology : CBP, 149(3), 427-432 (2008-11-06)
The differential expression of a set of genes encoding antioxidant enzymes and stress-responsive proteins was investigated by real-time quantitative PCR in intestine, liver, and muscle tissues extracted from Oryzias javanicus after exposure to the organophosphorus pesticide, Iprobenfos (IBP). After IBP
T Tsuda et al.
Comparative biochemistry and physiology. C, Comparative pharmacology and toxicology, 96(1), 23-26 (1990-01-01)
1. Bioconcentration and excretion of diazinon, IBP, malathion and fenitrothion were studied for carp (Cyprinus carpio L.). 2. The concentrations of these pesticides in muscle and viscera of the carp reached plateaus in 12-48 hr exposure. 3. The average values
Young Seop Kwon et al.
Analytica chimica acta, 868, 60-66 (2015-03-31)
The sensitive detection of iprobenfos (IBF) and edifenphos (EDI) was successfully conducted by using a new aptamer-based colorimetric multi-aptasensor. The dissociation constants of this multi-target aptamer to both iprobenfos and edifenphos were found to be 1.67 μM and 38 nM

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