392251
苯并[k]荧蒽
suitable 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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关于此项目
经验公式（希尔记法）:
C20H12
化学文摘社编号:
分子量:
252.31
Beilstein:
1873745
EC 号:
MDL编号:
UNSPSC代码:
12352103
PubChem化学物质编号:
NACRES:
NA.23
质量水平
方案
≥99%
mp
215-217 °C (lit.)
溶解性
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
适用性
suitable for fluorescence
SMILES字符串
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 key
HAXBIWFMXWRORI-UHFFFAOYSA-N
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应用
- Enhanced degradation of carcinogenic PAHs benzo (a) pyrene and benzo (k) fluoranthene by a microbial consortia：用微生物菌群生物修复高分子量多环芳烃(PAH)(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：苯并[k]荧蒽的生物转化和产物鉴定(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：研究苯并[k]荧蒽的电化学性质并开发检测方法(A Altun, Y Yardim, A Levent, 2023)。
包装
无底玻璃瓶。内含物装在锥底内插管中。
警示用语：
Danger
危险声明
危险分类
Aquatic Acute 1 - Aquatic Chronic 1 - Carc. 1B
储存分类代码
6.1C - Combustible acute toxic Cat.3 / toxic compounds or compounds which causing chronic effects
WGK
WGK 3
个人防护装备
Eyeshields, Gloves, type P3 (EN 143) respirator cartridges
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
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
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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