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Merck
CN

A805

苊烯

75%

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经验公式(希尔记法):
C12H8
化学文摘社编号:
分子量:
152.19
UNSPSC Code:
12352100
NACRES:
NA.22
PubChem Substance ID:
EC Number:
205-917-1
Beilstein/REAXYS Number:
774092
MDL number:
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产品名称

苊烯, 75%

SMILES string

c1cc2C=Cc3cccc(c1)c23

InChI key

HXGDTGSAIMULJN-UHFFFAOYSA-N

InChI

1S/C12H8/c1-3-9-4-2-6-11-8-7-10(5-1)12(9)11/h1-8H

assay

75%

form

solid

impurities

20% acenaphthene

bp

280 °C (lit.)

mp

78-82 °C (lit.)

density

0.899 g/mL at 25 °C (lit.)

Quality Level

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pictograms

Exclamation mark

signalword

Warning

Hazard Classifications

Acute Tox. 4 Oral - Eye Irrit. 2 - Skin Irrit. 2 - STOT SE 3

target_organs

Respiratory system

存储类别

11 - Combustible Solids

wgk

WGK 3

flash_point_f

251.6 °F - closed cup

flash_point_c

122.0 °C - closed cup

ppe

dust mask type N95 (US), Eyeshields, Gloves


历史批次信息供参考:

分析证书(COA)

Lot/Batch Number

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E Leonhardt et al.
Analytical chemistry, 70(6), 1228-1230 (1998-04-08)
Polycyclic aromatic hydrocarbons were extracted from a soil sample using ultrasound and dichloromethane-, cyclohexane-, and toluene-water mixtures. It was found that when dichloromethane is used as an extractant, acenaphthylene reacts with the solvent. Several chlorinated and oxygenated derivatives were identified.
Yan Hao et al.
Organic & biomolecular chemistry, 10(4), 724-728 (2011-12-15)
A simple and novel protocol for the efficient synthesis of a series of 8-carboxylnaphthyl functionalized pyrazolo[3,4-b]pyridine derivatives was developed through a one-pot, three-component reaction involving acenaphthylene-1,2-dione and 1H-pyrazol-5-amine in acetic acid medium. The reaction represents the first facile conversion of
K Schirmer et al.
Toxicology, 127(1-3), 129-141 (1998-08-12)
Sixteen polycyclic aromatic hydrocarbons (PAHs) were screened for their ability to be directly cytotoxic to a cell line from the rainbow trout gill, RTgill-W1. Exposure times of 2 h or less were sufficient for direct cytotoxicity to be detected, which
F J Rivas et al.
Journal of hazardous materials, 75(1), 89-98 (2000-06-01)
Removal of acenaphthylene from water has been carried out by means of different treatments combining UV radiation, ozone and hydrogen peroxide. Ozonation alone or in conjunction with hydrogen peroxide (10(-3) M) resulted in the highest elimination rates. Thus, conversions as
Siriwat Poonthrigpun et al.
Applied and environmental microbiology, 72(9), 6034-6039 (2006-09-08)
The acenaphthylene-degrading bacterium Rhizobium sp. strain CU-A1 was isolated from petroleum-contaminated soil in Thailand. This strain was able to degrade 600 mg/liter acenaphthylene completely within three days. To elucidate the pathway for degradation of acenaphthylene, strain CU-A1 was mutagenized by

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