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等級
certified reference material
agency
BCR®
製造商／商標名
JRC
技術
HPLC: suitable
gas chromatography (GC): suitable
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
形式
neat
儲存溫度
2-8°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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分析報告
For more information please see:
BCR048R
BCR048R
法律資訊
BCR is a registered trademark of European Commission
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
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.
Shan Chen et al.
Environmental science & technology, 42(24), 9431-9436 (2009-01-30)
Japanese medakas (Oryzias latipes) and triolein-embedded cellulose acetate membranes (TECAMs) were exposed simultaneously to benzo[k]fluoranthene (BkF) in the static exposure system containing different concentrations of humic acid (HA). The concentration-response relationships of induced hepatic 7-ethoxysorufin-o-deethylase (EROD) activity were established in
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