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
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
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.
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
Luqing Pan et al.
Comparative biochemistry and physiology. Toxicology & pharmacology : CBP, 141(3), 248-256 (2005-08-13)
Scallops (Chlamys ferrari) were cultured for 30 days in seawater containing benzo(k)fluoranthene (BkF) at 0.5, 1.0 and 10.0 microg/L. No effects were noted on 7-ethoxyresorufin O-deethylase (EROD) activity in digestive gland at low concentrations (0.5 and 1 microg/L) of BkF
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