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392251

Sigma-Aldrich

苯并[k]荧蒽

for fluorescence, ≥99%

同義詞:

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

經驗公式（希爾表示法）:
C20H12
CAS號碼:
207-08-9
分子量：:
252.31
Beilstein:
1873745
EC號碼:
205-916-6
MDL號碼:
MFCD00046287
分類程式碼代碼:
12352103
PubChem物質ID:
24864439
NACRES:
NA.23

等級

for fluorescence

品質等級

200

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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相關類別

應用


  • 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)。

包裝

无底玻璃瓶。内含物装在锥底内插管中。

象形圖

Health hazardEnvironment
GHS08,GHS09

訊號詞

Danger

危險聲明

H350,H410

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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分析證明 (COA)

Lot/Batch Number
BCCH2425
BCCG5267
BCCG3781
BCCD6599
BCCC3079

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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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