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Merck
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Documenti fondamentali

275336

Sigma-Aldrich

Benzo[b]fluoranthene

98%

Sinonimo/i:

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

Formula empirica (notazione di Hill):
C20H12
Numero CAS:
Peso molecolare:
252.31
Numero CE:
Numero MDL:
Codice UNSPSC:
12352100
ID PubChem:
NACRES:
NA.22

Saggio

98%

Stato

solid

Punto di fusione

163-165 °C (lit.)

Stringa SMILE

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
FTOVXSOBNPWTSH-UHFFFAOYSA-N

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Descrizione generale

The oxidative damage and bioaccumulation of juvenile scallops Chlamys farreri exposed to benzo[b]fluoranthene, a polycyclic aromatic hydrocarbon, was studied.

Benz[e]acephenanthrylene is a polycyclic aromatic hydrocarbon composed of a central 5-membered ring surrounded by four benzene rings.

Pittogrammi

Health hazardEnvironment

Avvertenze

Danger

Indicazioni di pericolo

Classi di pericolo

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

Codice della classe di stoccaggio

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

Classe di pericolosità dell'acqua (WGK)

WGK 3

Punto d’infiammabilità (°F)

Not applicable

Punto d’infiammabilità (°C)

Not applicable


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Chrysene

Sigma-Aldrich

769215

Chrysene

Meng Xiu et al.
Ecotoxicology and environmental safety, 107, 103-110 (2014-06-27)
The study is aimed at investigating the bioaccumulation and oxidative damage of juvenile scallops (Chlamys farreri) exposed to three selected PAHs: benzo[a]pyrene (BaP), benzo[b]fluoranthene (BbF) and chrysene (CHR). For this purpose, a study was performed on juvenile scallops exposed to
Shangbo Zhou et al.
The Science of the total environment, 763, 143030-143030 (2020-11-02)
Bioanalytical equivalents (BEQs) of mixtures and environmental samples are widely used to reflect the potential threat of pollutants in the environment and can be obtained by bioassays or using chemical analysis combined with relative potencies (REPs). In this study, the
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
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)
Thomas L Ter Laak et al.
Environmental science & technology, 43(19), 7212-7217 (2009-10-24)
In this study, the uptake of pyrene and benzo[b]fluoranthene by an aquatic worm (Lumbriculus variegatus) and a poly(dimethylsiloxane) coated glass fiber was studied at different humic acid concentrations. The accumulation of pyrene was not affected by the presence of the

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