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HomeProduct name listBenzo[k]fluoranthene

Benzo[k]fluoranthene

Synonym(s):11,12-Benzofluoranthene;2,3,1′,8′-Binaphthylene;8,9-Benzfluoranthene;Benzo[k]fluoranthene solution

  • CAS NO.:207-08-9
  • Empirical Formula: C20H12
  • Molecular Weight: 252.31
  • MDL number: MFCD00046287
  • EINECS: 205-916-6
  • SAFETY DATA SHEET (SDS)
  • Update Date: 2023-07-16 20:23:40
Benzo[k]fluoranthene Structural

What is Benzo[k]fluoranthene?

Chemical properties

yellow crystals

The Uses of Benzo[k]fluoranthene

Benzo[k]fluoranthene is used as an optical sensor for nitro-aromatic compounds due to fluorescence quenching of the molecule. It is also a carcinogen and mutagen.

What are the applications of Application

Benzo[k]fluoranthene is an optical sensor for nitro-aromatic compounds, chosen due to fluorescence quenching of the molecule.

Definition

ChEBI: Benzo[k]fluoranthene is a member of naphthalenes.

General Description

Pale yellow needles or yellow crystalline solid.

Air & Water Reactions

Insoluble in water.

Reactivity Profile

BENZO[K]FLUORANTHENE can react with strong oxidizing agents. May react with electrophiles, peroxides, nitrogen oxides and sulfur oxides

Hazard

Possible carcinogen.

Health Hazard

ACUTE/CHRONIC HAZARDS: When heated to decomposition BENZO(K)FLUORANTHENE emits acrid smoke and irritating fumes.

Health Hazard

Benzo[k]fluoranthene caused lungs and skincancers in animals. It produced tumors atthe site of application. Its carcinogenicity inhumans is not known.

Fire Hazard

Flash point data for BENZO(K)FLUORANTHENE are not available; however, BENZO(K)FLUORANTHENE is probably combustible.

Safety Profile

Confirmed carcinogen withexperimental tumorigenic data. Mutation data reported.When heated to decomposition it emits acrid smoke andirritating fumes.

Carcinogenicity

Benzo[k]fluoranthene wastested for carcinogenicity by dermal application in mice in one study, intraperitoneal injection into newborn mice in one study, and intrapulmonary implantation into rats in one study. Benzo[k]fluoranthene exhibited a significant carcinogenic activity in the dermal and intrapulmonary assays.

Source

Benzo[b]fluoranthene and benzo[k]fluoranthene were detected in 8 diesel fuels at concentrations ranging from 0.0027 to 3.1 mg/L with a mean value of 0.266 mg/L (Westerholm and Li, 1994). Also present in gasoline (9 μg/L), bitumen (34–1,140 μg/L), crude oil (<1 ppm) (quoted, Verschueren, 1983), and coal (32.5 g/kg) (Lao et al., 1975).
Based on laboratory analysis of 7 coal tar samples, benzo[k]fluoranthene concentrations ranged from 350 to 3,000 ppm (EPRI, 1990). Identified in high-temperature coal tar pitches used in roofing operations at concentrations ranging from 1,670 to 4,500 mg/kg (Malaiyandi et al., 1982).
Nine commercially available creosote samples contained benzo[k]fluoranthene at concentrations ranging from 2 to 67 mg/kg (Kohler et al., 2000).
Schauer et al. (2001) measured organic compound emission rates for volatile organic compounds, gas-phase semi-volatile organic compounds, and particle phase organic compounds from the residential (fireplace) combustion of pine, oak, and eucalyptus. The particle-phase emission rates of benzo[k]fluoranthene were 0.671 mg/kg of pine burned, 0.303 mg/kg of oak burned, and 0.286 mg/kg of eucalyptus burned.
California Phase II reformulated gasoline contained benzo[k]fluoranthene at a concentration of 280 μg/kg. Particle-phase tailpipe emission rate from a noncatalyst-equipped gasoline-powered automobile was 32.7 μg/km (Schauer et al., 2002).
Under atmospheric conditions, a low rank coal (0.5–1 mm particle size) from Spain was burned in a fluidized bed reactor at seven different temperatures (50 °C increments) beginning at 650 °C. The combustion experiment was also conducted at different amounts of excess oxygen (5 to 40%) and different flow rates (700 to 1,100 L/h). At 20% excess oxygen and a flow rate of 860 L/h, the amount of benzo[k]fluoranthene emitted ranged from 0 ng/kg at three temperatures (650, 750, and 950 °C) to 180.5 ng/kg at 850 °C. The greatest amount of PAHs emitted were observed at 750 °C (Mastral et al., 1999).

Environmental Fate

Soil. Based on aerobic soil die-away test data, the half-life in soil ranged from 910 d to 5.86 yr (Bossert et al., 1984).
Photolytic. The atmospheric half-life was estimated to range from 1.1 to 11 h (Atkinson, 1987). Chemical/Physical. Benzo[k]fluoranthene will not hydrolyze because it has no hydrolyzable functional group (Kollig, 1995).

Properties of Benzo[k]fluoranthene

Melting point: 215-217 °C(lit.)
Boiling point: 480 °C
Density  1.286
vapor pressure  9.59 x 10-11 mmHg at 25 °C (extrapolated from vapor pressures determined at higher temperatures, Puppet al., 1974)
refractive index  1.8390 (estimate)
Flash point: 100 °C
storage temp.  2-8°C
solubility  95% ethanol: <1mg/mL at 20°C
form  neat
pka >15 (Christensen et al., 1975)
color  Pale yellow needles
Water Solubility  1.09 μg/L at 25 °C (de Maagd et al., 1998)
BRN  1873745
Henry's Law Constant 2.17, 4.24, 10.56, 13.62, 19.54, and 39.77 at 10.0, 20.0, 35.0, 40.1, 45.0, and 55.0 °C, respectively (wetted-wall column, ten Hulscher et al., 1992)
Stability: Stable. Combustible. Incompatible with strong oxidizing agents.
CAS DataBase Reference 207-08-9(CAS DataBase Reference)
IARC 2B (Vol. 92) 2010
EPA Substance Registry System Benzo[k]fluoranthene (207-08-9)

Safety information for Benzo[k]fluoranthene

Signal word Danger
Pictogram(s)
ghs
Health Hazard
GHS08
ghs
Environment
GHS09
GHS Hazard Statements H350:Carcinogenicity
H410:Hazardous to the aquatic environment, long-term hazard
Precautionary Statement Codes P202:Do not handle until all safety precautions have been read and understood.
P273:Avoid release to the environment.
P280:Wear protective gloves/protective clothing/eye protection/face protection.
P391:Collect spillage. Hazardous to the aquatic environment
P308+P313:IF exposed or concerned: Get medical advice/attention.
P405:Store locked up.

Computed Descriptors for Benzo[k]fluoranthene

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