A805
Acenaphthylene
75%
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About This Item
Empirical Formula (Hill Notation):
C12H8
CAS Number:
Molecular Weight:
152.19
UNSPSC Code:
12352100
NACRES:
NA.22
PubChem Substance ID:
EC Number:
205-917-1
Beilstein/REAXYS Number:
774092
MDL number:
Assay:
75%
Form:
solid
form
solid
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%
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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Related Categories
signalword
Warning
hcodes
Hazard Classifications
Acute Tox. 4 Oral - Eye Irrit. 2 - Skin Irrit. 2 - STOT SE 3
target_organs
Respiratory system
Storage Class
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
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Zhiru Ma et al.
The journal of physical chemistry. A, 111(10), 2020-2027 (2007-03-29)
13C chemical shift tensor data from 2D FIREMAT spectra are reported for 4,7-di-t-butylacenaphthene and 4,7-di-t-butylacenaphthylene. In addition, calculations of the chemical shielding tensors were completed at the B3LYP/6-311G** level of theory. While the experimental tensor data on 4,7-di-t-butylacenaphthylene are in
N D Marsh et al.
Spectrochimica acta. Part A, Molecular and biomolecular spectroscopy, 56A(8), 1499-1511 (2000-07-25)
We have examined the UV spectra of six newly-synthesized ethynyl-PAH (1-ethynylnaphthalene, 5-ethynylacenaphthylene, 1-ethynylanthracene, 9-ethynylphenanthrene, 3-ethynylfluoranthene, and 1-ethynylpyrene) and five corresponding CP-PAH (acenaphthylene, aceanthrylene, acephenanthrylene, cyclopenta[cd]fluoranthene, and cyclopenta[cd]pyrene) and have found the following systematic behavior: ethynyl-substitution results in average bathochromic shifts
Onruthai Pinyakong et al.
FEMS microbiology letters, 238(2), 297-305 (2004-09-11)
Sphingomonas sp. strain A4 is capable of utilizing acenaphthene and acenaphthylene as sole carbon and energy sources, but it is unable to grow on other polycyclic aromatic hydrocarbons (PAHs). The genes encoding terminal oxygenase components of ring-hydroxylating dioxygenase (arhA1 and
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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