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Merck
CN

SCB-002

Supelco

Benzo[b]fluoranthene

vial of 1 g, analytical standard, Cerilliant®

Synonym(s):

2,3-Benzfluoranthene, 3,4-Benz[e]acephenanthrylene, 3,4-Benzfluoranthene, 3,4-Benzofluoranthene, Benz[e]acephenanthrylene, Benzo[e]fluoranthene, NSC 89265

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About This Item

Empirical Formula (Hill Notation):
C20H12
CAS Number:
205-99-2
Molecular Weight:
252.31
EC Number:
205-911-9
MDL number:
MFCD00010582
UNSPSC Code:
41116107
PubChem Substance ID:
329824646

Key Documents

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grade

analytical standard

packaging

vial of 1 g

manufacturer/tradename

Cerilliant®

mp

163-165 °C (lit.)

application(s)

environmental
forensics and toxicology

format

neat

storage temp.

room temp

SMILES string

c1ccc-2c(c1)-c3cccc4c3c-2cc5ccccc45

InChI

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

InChI key

FTOVXSOBNPWTSH-UHFFFAOYSA-N

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Legal Information

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

Pictograms

Health hazardEnvironment
GHS08,GHS09

Signal Word

Danger

Hazard Statements

H350,H410

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

Flash Point(F)

Not applicable

Flash Point(C)

Not applicable

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Certificates of Analysis (COA)

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Vapor phase and particulate bound polycyclic aromatic hydrocarbons in the smoke of mosquito coils.
J M Lin et al.
Bulletin of environmental contamination and toxicology, 59(6), 868-874 (1997-12-24)
Yeh-Chung Chien et al.
Archives of toxicology, 84(10), 767-776 (2010-06-24)
Although urinary 1-hydroxypyrene (1-OHP) is the most relevant parameter for assessing exposure to polycyclic aromatic hydrocarbons, the inability to further elucidate the intra- and inter-individual variability, specificity and kinetics makes it difficult to enhance its value as an exposure predictor.
Hitoshi Ishikawa et al.
Cancer letters, 240(1), 29-35 (2005-10-26)
Air pollution has been suggested to cause genetic damage from investigations of many biological markers that measure cytogenetic damage in humans. Here, we evaluated the genotoxic effects of ambient air pollution by investigating the extent of cytogenetic damage in human
H B Zhang et al.
Environmental pollution (Barking, Essex : 1987), 141(1), 107-114 (2005-10-26)
Surface soil (0-10 cm) samples from 53 sampling sites including rural and urban areas of Hong Kong were collected and analyzed for 16 EPA priority polycyclic aromatic hydrocarbons (PAHs). Total PAH concentrations were in the range of 7.0-410 microg kg(-1)
S Aubin et al.
Journal of the Air & Waste Management Association (1995), 50(12), 2093-2101 (2001-01-05)
Benzo[b]fluoranthene (B[b]F) was used in relative abundance ratios (RARs), a parameter obtained by dividing the concentration of individual polycyclic aromatic hydrocarbons (PAHs) found in a given sample by the concentration of B[b]F in the same sample. The B[b]F RARs were
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