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BCR048R

Benzo[k]fluoranthene

BCR®, certified reference material

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About This Item

Empirical Formula (Hill Notation):
C20H12
CAS Number:
Molecular Weight:
252.31
Beilstein:
1873745
EC Number:
MDL number:
UNSPSC Code:
41116107
PubChem Substance ID:
NACRES:
NA.24

grade

certified reference material

Agency

BCR®

manufacturer/tradename

JRC

technique(s)

HPLC: suitable
gas chromatography (GC): suitable

mp

215-217 °C (lit.)

solubility

95% ethanol: <1 mg/mL at 20 °C
DMSO: <1 mg/mL at 20 °C
H2O: <1 mg/mL at 20 °C
acetone: 1-10 mg/mL at 20 °C
methanol: <1 mg/mL at 20 °C
toluene: 5-10 mg/mL at 20 °C

format

neat

storage temp.

2-8°C

SMILES string

c1ccc2cc-3c(cc2c1)-c4cccc5cccc-3c45

InChI

1S/C20H12/c1-2-6-15-12-19-17-10-4-8-13-7-3-9-16(20(13)17)18(19)11-14(15)5-1/h1-12H

InChI key

HAXBIWFMXWRORI-UHFFFAOYSA-N

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Analysis Note

For more information please see:
BCR048R

Legal Information

BCR is a registered trademark of European Commission

Pictograms

Health hazardEnvironment

Signal Word

Danger

Hazard Statements

Hazard Classifications

Aquatic Acute 1 - Aquatic Chronic 1 - Carc. 1B

Storage Class Code

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

WGK

WGK 3

Personal Protective Equipment

dust mask type N95 (US), Eyeshields, Gloves

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K L Willett et al.
Toxicology and applied pharmacology, 177(3), 264-271 (2001-12-26)
Certainpolynuclear aromatic hydrocarbons (PAHs) such as benzo[a]pyrene (BaP) induce CYP1A-dependent enzyme activities. Because PAHs are ubiquitous environmental contaminants, and some are aryl hydrocarbon agonists, CYP1A has been used as a biomarker for PAH exposure. However, PAHs exist in the environment
Hiroyuki Masaki et al.
The Analyst, 130(9), 1253-1257 (2005-08-13)
We developed a device and some systems for detecting benzo[a]pyrene (B[a]P) and benzo[k]fluoranthene (B[k]F). The device uses a UV light-emitting diode that emits light with a wavelength of 370 nm and a violet laser diode that emits light with a
Petra Booij et al.
Environmental toxicology and chemistry, 30(4), 898-904 (2010-12-31)
In bioassays, exposure concentrations of test compounds are usually expressed as nominal concentrations. As a result of various processes, such as adsorption, degradation, or uptake, the actual freely dissolved concentration of the test compound may differ from the nominal concentration.
Annekatrin Dreyer et al.
Environmental science & technology, 39(11), 3918-3924 (2005-06-30)
To date, studies about historic PAH (polycyclic aromatic hydrocarbons) deposition at a regional scale have rarely been published. To address this research gap, we sampled 17 ombrotrophic peatlands across eastern Canada. The peat cores from hollows were dated with 210Pb
David C Spink et al.
Toxicology and applied pharmacology, 226(3), 213-224 (2007-10-09)
The interactions of polycyclic aromatic hydrocarbons (PAH) and cytochromes P450 (CYP) are complex; PAHs are enzyme inducers, substrates, and inhibitors. In T-47D breast cancer cells, exposure to 0.1 to 1 microM benzo(k)fluoranthene (BKF) induced CYP1A1/1B1-catalyzed 17beta-estradiol (E(2)) metabolism, whereas BKF

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