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About This Item
Empirical Formula (Hill Notation):
C12H8
CAS Number:
Molecular Weight:
152.19
Beilstein:
774092
EC Number:
MDL number:
UNSPSC Code:
12352100
PubChem Substance ID:
NACRES:
NA.22
Recommended Products
Quality Level
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.)
SMILES string
c1cc2C=Cc3cccc(c1)c23
InChI
1S/C12H8/c1-3-9-4-2-6-11-8-7-10(5-1)12(9)11/h1-8H
InChI key
HXGDTGSAIMULJN-UHFFFAOYSA-N
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Signal Word
Warning
Hazard Statements
Precautionary Statements
Hazard Classifications
Acute Tox. 4 Oral - Eye Irrit. 2 - Skin Irrit. 2 - STOT SE 3
Target Organs
Respiratory system
Storage Class Code
11 - Combustible Solids
WGK
WGK 3
Flash Point(F)
251.6 °F - closed cup
Flash Point(C)
122.0 °C - closed cup
Personal Protective Equipment
dust mask type N95 (US), Eyeshields, Gloves
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Dong Wang et al.
The Journal of organic chemistry, 71(22), 8365-8371 (2006-10-27)
Polycyclic aromatic hydrocarbon growth from acenaphthylene and cyclopentadienyl was investigated by using the B3LYP/6-31G(d,p) and BH&HLYP/6-31G(d,p) levels of theory as well as transition state theory. The reaction pathways of cyclopentadienyl bearing hydrocarbons are different from those without these moieties and
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
Ming Chen et al.
Chemical communications (Cambridge, England), (9)(9), 1112-1114 (2008-02-23)
A higher efficiency of excitation energy transfer occurs to a luminescent diphenylanthracenyl acceptor incorporated at the centre, rather than the end, of an acenaphthylene polymer chain.
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
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
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