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Merck

392251

Sigma-Aldrich

苯并[k]荧蒽

for fluorescence, ≥99%

别名:

11,12-苯并荧蒽, 2,3,1′,8′-联萘, 8,9-苯并荧蒽

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About This Item

经验公式(希尔记法):
C20H12
CAS号:
分子量:
252.31
Beilstein:
1873745
EC號碼:
MDL號碼:
分類程式碼代碼:
12352103
PubChem物質ID:
NACRES:
NA.23

等級

for fluorescence

品質等級

化驗

≥99%

mp

215-217 °C (lit.)

溶解度

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

SMILES 字串

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 密鑰

HAXBIWFMXWRORI-UHFFFAOYSA-N

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應用


  • Enhanced degradation of carcinogenic PAHs benzo (a) pyrene and benzo (k) fluoranthene by a microbial consortia: Bioremediation of high molecular weight PAHs with a combination of microorganisms (S Guntupalli, V Thunuguntla, 2016).

  • Biotransformation of the high‐molecular weight polycyclic aromatic hydrocarbon (PAH) benzofluoranthene by Sphingobium sp. strain KK22 and identification of metabolites: Biotransformation and identification of products from benzo[k]fluoranthene (AH Maeda, S Nishi, Y Hatada, Y Ozeki, 2014).

  • Investigation of the electrochemical properties of benzofluorenthene using a glassy carbon electrode and development of a square-wave voltammetric method for detection: Electrochemical behavior of benzo[k]fluorenthene and development of detection method (A Altun, Y Yardim, A Levent, 2023).

包裝

无底玻璃瓶。内含物装在锥底内插管中。

象形圖

Health hazardEnvironment

訊號詞

Danger

危險聲明

危險分類

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

儲存類別代碼

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

水污染物質分類(WGK)

WGK 3

個人防護裝備

Eyeshields, Gloves, type P3 (EN 143) respirator cartridges


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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
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
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.
Alberto Modelli et al.
The journal of physical chemistry. A, 110(20), 6482-6486 (2006-05-19)
The gas-phase experimental adiabatic electron affinities (AEAs) of the polycyclic aromatic hydrocarbons (PAHs) anthracene, tetracene, pentacene, chrysene, pyrene, benzo[a]pyrene, benzo[e]pyrene, and fluoranthene are well reproduced using the hybrid density functional method B3LYP with the 6-31+G* basis set, indicating that the

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