Welcome to LookChem.com Sign In|Join Free
  • or
BENZO(K)FLUORANTHENE, also known as 8,9-benzfluoranthene, 8,9-benzofluoranthene, 1 1.12-benzofiuoranthene, 2,3,1,8-binaphthylene, and dibenzo(bjk)fluorene, is a pale yellow crystalline solid with a molecular weight of 252.32 and a molecular formula of C20H12. It is characterized by four benzene rings in various configurations containing only carbon and hydrogen atoms. It is absorbed through the skin, lungs, and gastrointestinal tract and is considered an environmental pollutant in industrial processes.

207-08-9

Post Buying Request

207-08-9 Suppliers

Recommended suppliers

  • Product
  • FOB Price
  • Min.Order
  • Supply Ability
  • Supplier
  • Contact Supplier

207-08-9 Usage

Uses

Used in Environmental Monitoring:
BENZO(K)FLUORANTHENE is used as an optical sensor for nitro-aromatic compounds due to the fluorescence quenching of the molecule. This property allows it to detect the presence of these compounds, which are often associated with environmental contamination and can pose health risks.
Used in Toxicology Research:
As a known carcinogen and mutagen, BENZO(K)FLUORANTHENE is utilized in toxicology research to study the effects of exposure to such harmful substances. Understanding its impact on biological systems can help in developing methods to mitigate its harmful effects and improve environmental and public health safety.

Clinical Trial

B(k)F is a weak carcinogen in mice and is also a weak tumor initiator. It is very much weaker than benzo(a)pyrene (BP). The observations regarding systemic tumors following topical application of these carcinogens to mice is of great importance. All too frequently, a dermal carcinogenicity study concentrates on skin tumors and no others. Thus, it is relatively unusual to have systemic tumors investigated. The fact that there was no difference in the level of systemic tumors in all groups, including the potent mouse carcinogen BP, would indicate that the level of systemic absorption through the skin was not significant.

Health Toxicity

B(k)F could penetrate the skin of some animals, especially mice, and remain present for a number of hours. The metabolism of B(k)F appears to follow a route leading to the predominant formation of its 5-hydroxy derivative. The further metabolism of this phenolic dihydrodiol to 5,9,10,trihydroxy-l1, 12-epoxy-9,10,11,12-tetrahydro- benzo(k)fluoranthene has been linked to the genotoxic effect of B(k)F in mouse skin. Care was taken to avoid contact with the head, axillae, and genital areas.

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

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

Health Hazard

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

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]fluoranthenewastested 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).

Check Digit Verification of cas no

The CAS Registry Mumber 207-08-9 includes 6 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 3 digits, 2,0 and 7 respectively; the second part has 2 digits, 0 and 8 respectively.
Calculate Digit Verification of CAS Registry Number 207-08:
(5*2)+(4*0)+(3*7)+(2*0)+(1*8)=39
39 % 10 = 9
So 207-08-9 is a valid CAS Registry Number.
InChI: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

207-08-9 Well-known Company Product Price

  • Brand
  • (Code)Product description
  • CAS number
  • Packaging
  • Price
  • Detail
  • Supelco

  • (48668)  Benzo[k]fluoranthenesolution  200 μg/mL in methylene chloride, certified reference material

  • 207-08-9

  • 000000000000048668

  • 272.61CNY

  • Detail
  • Aldrich

  • (392251)  Benzo[k]fluoranthene  for fluorescence, ≥99%

  • 207-08-9

  • 392251-100MG

  • 1,695.33CNY

  • Detail
  • Supelco

  • (48492)  Benzo[k]fluoranthene  analytical standard

  • 207-08-9

  • 000000000000048492

  • 764.01CNY

  • Detail
  • Supelco

  • (40073)  Benzo[k]fluoranthenesolution  certified reference material, 1000 μg/mL in acetone

  • 207-08-9

  • 000000000000040073

  • 359.19CNY

  • Detail
  • Sigma-Aldrich

  • (BCR048R)  Benzo[k]fluoranthene  BCR® certified Reference Material

  • 207-08-9

  • BCR048R-10MG

  • 1,705.86CNY

  • Detail
  • Supelco

  • (49476-U)  Benzo(k)fluoranthenesolution  100 μg/mL in methylene chloride, analytical standard

  • 207-08-9

  • 49476-U

  • 294.84CNY

  • Detail

207-08-9SDS

SAFETY DATA SHEETS

According to Globally Harmonized System of Classification and Labelling of Chemicals (GHS) - Sixth revised edition

Version: 1.0

Creation Date: Aug 13, 2017

Revision Date: Aug 13, 2017

1.Identification

1.1 GHS Product identifier

Product name benzo[k]fluoranthene

1.2 Other means of identification

Product number -
Other names Benzo<k>fluoranthene

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only.
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
Service hours Monday to Friday, 9am-5pm (Standard time zone: UTC/GMT +8 hours).

More Details:207-08-9 SDS

207-08-9Synthetic route

C20H14O

C20H14O

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With zinc(II) chloride In acetic anhydride at 130℃; for 0.5h;88%
2-hydroxy-3-(1-naphthyl)naphthalene triflate
146746-48-7

2-hydroxy-3-(1-naphthyl)naphthalene triflate

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With 1,8-diazabicyclo[5.4.0]undec-7-ene; lithium chloride; bis(triphenylphosphine)palladium(II)-chloride In N,N-dimethyl-formamide at 120℃; for 3h;64%
7-(methylthio)benzo[k]fluoranthene

7-(methylthio)benzo[k]fluoranthene

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
Raney Ni (W2) In ethanol for 6h; Heating;61%
(E)-1-ethynyl-8-styrylnaphthalene

(E)-1-ethynyl-8-styrylnaphthalene

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
In toluene at 140℃; for 24h; Sealed tube;54%
acenaphthenequinone monoxime
33489-49-5

acenaphthenequinone monoxime

o-xylylene(bistriphenylphospine) dibromide
1519-46-6

o-xylylene(bistriphenylphospine) dibromide

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With lithium ethoxide In N,N-dimethyl-formamide 1.) warming to 90 deg C, 5h; 2.)25 deg C, 12h;32%
azuleno<1,2-a>acenaphthylene
33084-86-5

azuleno<1,2-a>acenaphthylene

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

Conditions
ConditionsYield
In benzene at 600℃;A 14%
B 28%
[1,2′-binaphthalen]-8-yl nonafluorobutanesulfonate

[1,2′-binaphthalen]-8-yl nonafluorobutanesulfonate

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

Conditions
ConditionsYield
With dicyclohexyl-(2',6'-dimethoxybiphenyl-2-yl)-phosphane; potassium phosphate; tris-(dibenzylideneacetone)dipalladium(0); 1-Adamantanecarboxylic acid In N,N-dimethyl acetamide at 110℃; for 24h; Inert atmosphere;A 26%
B 8%
o-xylylene(bistriphenylphospine) dibromide
1519-46-6

o-xylylene(bistriphenylphospine) dibromide

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With sodium methylate In N,N-dimethyl-formamide at 0 - 20℃; for 3.5h; Wittig Olefination; Inert atmosphere;19%
With lithium hydroxide In dichloromethane for 48h; Ambient temperature;18%
Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With selenium at 340℃;
Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

PERYLENE

PERYLENE

C

cyclopenta[c,d]pyrene
27208-37-3

cyclopenta[c,d]pyrene

D

benzo[ghi]fluoranthene
203-12-3

benzo[ghi]fluoranthene

Conditions
ConditionsYield
at 1200℃; under 0.01 Torr; flash vacuum thermolysis; Further byproducts given;A 15 % Chromat.
B 7 % Chromat.
C 7 % Chromat.
D 4 % Chromat.
Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

PERYLENE
198-55-0

PERYLENE

C

cyclopenta[c,d]pyrene
27208-37-3

cyclopenta[c,d]pyrene

D

cyclopentacepyrylene
98791-43-6

cyclopentacepyrylene

Conditions
ConditionsYield
at 1200℃; under 0.01 Torr; flash vacuum thermolysis; Further byproducts given;A 15 % Chromat.
B 7 % Chromat.
C 7 % Chromat.
D 6 % Chromat.
at 1200℃; under 0.01 Torr; flash vacuum thermolysis; Further byproducts given;A 15 % Chromat.
B 13 % Chromat.
C 7 % Chromat.
D 6 % Chromat.
Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

PERYLENE
198-55-0

PERYLENE

C

benzo[ghi]fluoranthene
203-12-3

benzo[ghi]fluoranthene

D

benzacephenanthrylene
216-48-8

benzacephenanthrylene

Conditions
ConditionsYield
at 1200℃; under 0.01 Torr; flash vacuum thermolysis; Further byproducts given;A 15 % Chromat.
B 7 % Chromat.
C 4 % Chromat.
D 4 % Chromat.
Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

PERYLENE
198-55-0

PERYLENE

C

benzacephenanthrylene
216-48-8

benzacephenanthrylene

D

cyclopentacepyrylene
98791-43-6

cyclopentacepyrylene

Conditions
ConditionsYield
at 1200℃; under 0.01 Torr; flash vacuum thermolysis; Further byproducts given;A 15 % Chromat.
B 7 % Chromat.
C 4 % Chromat.
D 6 % Chromat.
U.S. low sulfur petroleum diesel fuel

U.S. low sulfur petroleum diesel fuel

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
combustion; Formation of xenobiotics;
100 percent soy methyl ester biodiesel fuel

100 percent soy methyl ester biodiesel fuel

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
combustion; Formation of xenobiotics;
methyl chloride; methane; mixture of

methyl chloride; methane; mixture of

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics;
polystyrene

polystyrene

A

phenanthridine
229-87-8

phenanthridine

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

PERYLENE
198-55-0

PERYLENE

D

cyclopenta[c,d]pyrene
27208-37-3

cyclopenta[c,d]pyrene

Conditions
ConditionsYield
With air at 900℃; Condensation; combustion; pyrolysis; PAH formation; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;A 0.04 mg
B 0.04 mg
C 0.12 mg
D 0.03 mg
polystyrene

polystyrene

A

11H-benzo[a]carbazole
239-01-0

11H-benzo[a]carbazole

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

Tetracen
92-24-0

Tetracen

D

cyclopenta[c,d]pyrene
27208-37-3

cyclopenta[c,d]pyrene

Conditions
ConditionsYield
With air at 900℃; Condensation; combustion; pyrolysis; PAH formation; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;A 0.21 mg
B 0.04 mg
C 0.45 mg
D 0.03 mg
polyethylene

polyethylene

A

2,2'-binaphthalene
612-78-2

2,2'-binaphthalene

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

benzopyrene
50-32-8

benzopyrene

D

1-phenyl phenanthrene
4325-76-2

1-phenyl phenanthrene

Conditions
ConditionsYield
With air at 600 - 900℃; Oxidation; Formation of xenobiotics; Further byproducts given;
waste wood chips

waste wood chips

A

benzo[e]acephenanthrylene
205-99-2

benzo[e]acephenanthrylene

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

chrysene
218-01-9

chrysene

D

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics; Further byproducts given;
benzofluoranthene-dicarboxylic acid-(7.12)-diamide

benzofluoranthene-dicarboxylic acid-(7.12)-diamide

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
With phosphoric acid at 150℃;
binaphthyl-(1.2')

binaphthyl-(1.2')

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

Conditions
ConditionsYield
With chromium corundum at 500℃;
1-(naphthalen-2-yl)naphthalene
4325-74-0

1-(naphthalen-2-yl)naphthalene

chromium oxide-aluminium oxide

chromium oxide-aluminium oxide

A

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

B

Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

Conditions
ConditionsYield
at 500℃;
phosphoric acid
86119-84-8, 7664-38-2

phosphoric acid

benzo[k]fluoranthene-7,12-dicarboxamide
875241-60-4

benzo[k]fluoranthene-7,12-dicarboxamide

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
at 150℃;
Eucalyptus grandis wood

Eucalyptus grandis wood

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

Conditions
ConditionsYield
Decomposition; Formation of xenobiotics; pyrolysis;
Pennzoil Perfomax SAE 5W-40 synthetic oil

Pennzoil Perfomax SAE 5W-40 synthetic oil

leaded gasoline 91 octane

leaded gasoline 91 octane

A

benzo[e]acephenanthrylene
205-99-2

benzo[e]acephenanthrylene

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

fluoranthene
206-44-0

fluoranthene

D

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
Mogul Forte GX SAE 15W-40 mineral oil

Mogul Forte GX SAE 15W-40 mineral oil

leaded gasoline 91 octane

leaded gasoline 91 octane

A

benzo[e]acephenanthrylene
205-99-2

benzo[e]acephenanthrylene

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

fluoranthene
206-44-0

fluoranthene

D

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
artificial solid municipal waste

artificial solid municipal waste

A

benzo[e]acephenanthrylene
205-99-2

benzo[e]acephenanthrylene

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

phenanthrene
85-01-8

phenanthrene

D

fluoranthene
206-44-0

fluoranthene

Conditions
ConditionsYield
With air at 780℃; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
tyre rubber

tyre rubber

A

benzo[e]acephenanthrylene
205-99-2

benzo[e]acephenanthrylene

B

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

C

fluoranthene
206-44-0

fluoranthene

D

benz[a]anthracene
56-55-3

benz[a]anthracene

Conditions
ConditionsYield
With carbon dioxide at 900℃; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

acetyl chloride
75-36-5

acetyl chloride

3-acetylbenzo[k]fluoranthene
1433843-55-0

3-acetylbenzo[k]fluoranthene

Conditions
ConditionsYield
With aluminum (III) chloride In dichloromethane at -5 - 0℃; Friedel-Crafts Acylation;68%
Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

A

benzo[k]fluoranthene-7,12-dione
112575-90-3

benzo[k]fluoranthene-7,12-dione

B

Benzo[k]fluoranthene-2,3-dione
112575-91-4

Benzo[k]fluoranthene-2,3-dione

Conditions
ConditionsYield
With cerium(IV) ammonium sulphate; sulfuric acid In acetonitrile for 5h; Ambient temperature;A 28%
B 10%
Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

benzo[k]fluoranthene-7,12-dione
112575-90-3

benzo[k]fluoranthene-7,12-dione

Conditions
ConditionsYield
With chromium(VI) oxide; acetic acid
Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

2,2-Dimethylmalonyl chloride
5659-93-8

2,2-Dimethylmalonyl chloride

2,2-dimethyl-2H-benzo[cd,k]fluoranthene-1,3-dione
325148-65-0

2,2-dimethyl-2H-benzo[cd,k]fluoranthene-1,3-dione

Benzo[k]fluoranthene
207-08-9

Benzo[k]fluoranthene

A

Benzo[j]fluoranthene
205-82-3

Benzo[j]fluoranthene

B

Benzacephenanthrylene
212-41-9

Benzacephenanthrylene

Conditions
ConditionsYield
at 1200℃; under 0.01 Torr; flash vacuum thermolysis;A 11 % Chromat.
B 5 % Chromat.

207-08-9Relevant academic research and scientific papers

Exploring the chemistry of a double-stranded cycle with the carbon skeleton of the belt region of the C84 fullerene

Stuparu, Mihaiela,Lentz, Dieter,Rueegger, Heinz,Schlueter, A. Dieter

, p. 88 - 100 (2007)

Intense scale-up efforts greatly improved the availability of the known double-stranded cycle 2 with two bridging ether units. The chemistry of 2 towards Bronsted and Lewis acids could, therefore, be investigated quite comprehensively. It was discovered that the reactivity of 2, whose carbon framework resembles the belt region of the C84 (D2) fullerene, is rather unusual as compared with acyclic model compounds. Whereas the latter could easily be dehydrated to the corresponding planar arenes, the former gave rise to a bouquet of unexpected reactions, which all avoided the aromatization of 2 to its still-elusive, fully conjugated congener B. Intermediates generated from 2 under acidic conditions attack the solvent (e.g. toluene) to give 4, form bridging lactones to give 11 or close back to starting material 2 (e.g. from 16) rather than dehydrate to more highly conjugated structures on the way to the fully unsaturated target cycle B. The structure of compound 4 was solved by X-ray diffraction. Through the reactions of 2 with Lewis acids, derivatives 14 and 15 became accessible. They are candidates for future attempts to achieve the desired aromatization under basic conditions or by thermal treatment. Wiley-VCH Verlag GmbH & Co. KGaA, 2007.

Ruthenium-Catalyzed Peri- and Ortho-Alkynylation with Bromoalkynes via Insertion and Elimination

Tan, Eric,Konovalov, Andrey I.,Fernández, Gabriela A.,Dorel, Ruth,Echavarren, Antonio M.

, p. 5561 - 5564 (2017)

The alkynylation of naphthols takes place with total regiocontrol at the peri position of the hydroxyl group in the presence of [RuCl2(p-cymene)]2 as the catalyst. This reaction features high functional group tolerance. The related o

Three-Step Synthesis of Fluoranthenes through Pd-Catalyzed Inter- and Intramolecular C-H Arylation

Yamaguchi, Miyuki,Higuchi, Mayu,Tazawa, Kanae,Manabe, Kei

, p. 3967 - 3974 (2016/05/24)

A three-step synthetic method for the preparation of fluoranthenes, involving Miura's intermolecular C-H arylation, nonaflation, and intramolecular C-H arylation, has been developed. Various 1-naphthols and haloarenes were successfully used as substrates. Reaction conditions that afford high site selectivity have been developed for the intramolecular C-H arylation step.

Scholl Cyclizations of Aryl Naphthalenes: Rearrangement Precedes Cyclization

Skraba-Joiner, Sarah L.,McLaughlin, Erin C.,Ajaz, Aida,Thamatam, Rajesh,Johnson, Richard P.

, p. 9578 - 9583 (2015/10/12)

In 1910, Scholl, Seer, and Weitzenbock reported the AlCl3-catalyzed cyclization of 1,1′-binaphthyl to perylene. We provide evidence that this classic organic name reaction proceeds through sequential and reversible formation of 1,2′- and 2,2′-binaphthyl isomers. Acid-catalyzed isomerization of 1,1′-binaphthyl to 2,2′-binaphthyl has been noted previously. The superacid trifluoromethanesulfonic acid (TfOH), 1 M in dichloroethane, catalyzes these rearrangements, with slower cyclization to perylene. Minor cyclization products are benzo[k]fluoranthene and benzo[j]fluoranthene. At ambient temperature, the observed equilibrium ratio of 1,1′-binaphthyl, 1,2′-binaphthyl, and 2,2′-binaphthyl is 1:3:97. DFT calculations with the inclusion of solvation support a mechanistic scheme in which ipso-arenium ions are responsible for rearrangements; however, we cannot distinguish between arenium ion and radical cation mechanisms for the cyclization steps. Under similar reaction conditions, 1-phenylnaphthalene interconverts with 2-phenylnaphthalene, with the latter favored at equilibrium (5:95 ratio), and also converts slowly to fluoranthene. Computations again support an arenium ion mechanism for rearrangements.

NMR and DFT study on onium ions derived from substituted fluoranthenes and benzo[κ]fluoranthenes

Okazaki, Takao,Adachi, Taisuke,Kitagawa, Toshikazu

, p. 464 - 471 (2013/05/22)

Fluoranthene and benzo[k]fluoranthene (3) are nonalternant polyaromatic hydrocarbons. Their derivatives, 3-acetyl, 8-acetyl, 3-nitro, and 3-aminofluoranthenes (4, 5, 7, and 8) were reacted in FSO3H/SO 2ClF and the solutions were observed by NMR measurements at low temperatures, which showed the formation of PAH-substituted onium ions. The most deshielded 13C peaks in fluoranthene frames were observed at 155.7 and 148.7 ppm for 4H+, 154.4 ppm for 5H+, 159.1 and 139.6 ppm for 7H+, and 139.7 ppm for 8H+. Distribution of the positive charges were estimated on the basis of changes in 13CNMR chemical shifts between onium ions and their corresponding parent compounds. Only limited delocalization of positive charges into the aromatic rings was found to occur. GIAO-derived NMR chemical shifts calculated by the DFT method were generally consistent with the experimental chemical shifts. DFT calculations suggested that benzo[k]fluoranthene (3) is favored to be protonated at C-3/C-7 positions. GIAO-derived NICS(1)zz were computed to elucidate aromaticity/antiaromaticity, and the results suggested that the five-membered rings are antiaromatic for cations 4H+, 7H+, 8H +, and 3aH+ (3-benzo[k]fluoranthenium ion).

Role of temperature and hydrochloric acid on the formation of chlorinated hydrocarbons and polycyclic aromatic hydrocarbons during combustion of paraffin powder, polymers, and newspaper

Takasuga, Takumi,Umetsu, Norihito,Makino, Tetsuya,Tsubota, Katsuya,Sajwan, Kenneth S.,Kumar, Kurunthachalam Senthil

, p. 8 - 21 (2008/02/09)

Formation of chlorinated hydrocarbons and polycyclic aromatic hydrocarbons (PAHs) were determined using a laboratory-scale incinerator when combusting materials at different temperatures, different concentrations of hydrochloric acid (HCl), and when combusting various types of polymers/newspaper. Polychlorobenzenes (PCBz), polychlorophenols (PCPhs), polychlorinated dibenzo-p-dioxins/furans (PCDD/Fs) and their toxic equivalency (TEQ) and PAHs were highlighted and reported. Our results imply maximum formation of chlorinated hydrocarbons at 400°C in the following order; PCBz≥PCPhs?PCDFs>PCDDs>TEQ on a parts-per-billion level. Similarly, a maximum concentration of chlorinated hydrocarbons was noticed with an HCl concentration at 1000 ppm with the presence of paraffin powder in the following order; PAHs>PCBz≥PCPhs?PCDFs>PCDDs>TEQ an a parts-per-billion level. PAHs were not measured at different temperatures. Elevated PAHs were noticed with different HCl concentrations and paraffin powder combustion (range: 27-32 μg/g). While, different polymers and newspaper combusted, nylon and acrylonitrile butadiene styrene (ABS) produced the maximum hydrogen cyanide (HCN) concentration, concentrations of PCDD/FS, dioxin-like polychlorinated biphenyls (DL-PCBs), and TEQ were in a decreasing order: polyvinylchloride (PVC)newspaperpolyethyleneterephthalate (PET) polyethylene (PE) polypropylene (PP) ABS = blank. Precursors of PCBs were in a decreasing order: PPnylonPEnewspaperABSPVCblankPET. Precursors of PCDD/Fs were in a decreasing order: newspaper PP= nylonPEABSPVC= blankPET. BTX formation was in a decreasing order; PEnylonnewspaperABSPP. PAHs formation were elevated with parts-per-million levels in the decreasing order of PPnylonPE newspaperblankABS PETPVC.

Emission factors and importance of PCDD/Fs, PCBs, PCNs, PAHs and PM 10 from the domestic burning of coal and wood in the U.K.

Lee, Robert G. M.,Coleman, Peter,Jones, Joanne L.,Jones, Kevin C.,Lohmann, Rainer

, p. 1436 - 1447 (2007/10/03)

This paper presents emission factors (EFs) derived for a range of persistent organic pollutants (POPs) when coal and wood were subject to controlled burning experiments, designed to simulate domestic burning for space heating. A wide range of POPs were emitted, with emissions from coal being higher than those from wood. Highest EFs were obtained for particulate matter, PM10, (~ 10 g/kg fuel) and polycyclic aromatic hydrocarbons (~ 100 mg/ kg fuel for ΣPAHs). For chlorinated compounds, EFs were highest for polychlorinated biphenyls (PCBs), with polychlorinated naphthalenes (PCNs), dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) being less abundant. EFs were on the order of 1000 ng/kg fuel for ΣPCBs, 100s ng/ kg fuel for ΣPCNs and 100 ng/kg fuel for ΣPCDD/Fs. The study confirmed that mono- to trichlorinated dibenzofurans, Cl1,2,3DFs, were strong indicators of low temperature combustion processes, such as the domestic burning of coal and wood. It is concluded that numerous PCB and PCN congeners are routinely formed during the combustion of solid fuels. However, their combined emissions from the domestic burning of coal and wood would contribute only a few percent to annual U.K. emission estimates. Emissions of PAHs and PM 10 were major contributors to U.K. national emission inventories. Major emissions were found from the domestic burning for Cl1,2,3DFs, while the contribution of PCDD/F-ΣTEQ to total U.K. emissions was minor.

Experimental study on the removal of PAHs using in-duct activated carbon injection

Zhou, Hong-Cang,Zhong, Zhao-Ping,Jin, Bao-Sheng,Huang, Ya-Ji,Xiao, Rui

, p. 861 - 869 (2007/10/03)

This paper presents the incineration tests of municipal solid waste (MSW) in a fluidized bed and the adsorption of activated carbon (AC) on polycyclic aromatic hydrocarbons (PAHs). An extraction and high performance liquid chromatography (HPLC) technique was used to analyze the concentrations of the 16 US EPA specified PAHs contained in raw MSW, flue gas, fly ash, and bottom ash. The aim of this work was to decide the influence of AC on the distribution of PAHs during the incineration of MSW. Experimental researches show that there were a few PAHs in MSW and bottom ash. With the increase of AC feeding rate, the concentrations of three- to six-ring PAHs in fly ash increased, and the concentration of two-ring PAH decreased. The total-PAHs in flue gas were dominated by three-, and four-ring PAHs, but a few two-, five-ring PAHs and no six-ring PAHs were found. PAHs could be removed effectively from flue gas by using in-duct AC injection and the removal efficiencies of PAHs were about 76-91%. In addition, the total toxic equivalent (TEQ) concentrations of PAH in raw MSW, bottom ash, fly ash, and flue gas were 1.24 mg TEQ kg-1, 0.25 mg TEQ kg-1, 6.89-9.67 mg TEQ kg-1, and 0.36-1.50 μg TEQ N m-3, respectively.

Efficient routes to acenaphthylene-fused polycyclic arenes/heteroarenes and heterocyclic fluoranthene analogues

Panda, Kausik,Venkatesh, Chelvam,Ila, Hiriyakkanavar,Junjappa, Hiriyakkanavar

, p. 2045 - 2055 (2007/10/03)

The acenaphthenone-derived a-oxoketene dithioacetal 2 has been subjected to various [3 + 3] aromatic and heteroaromatic annulation and other heterocyclization reactions previously developed in our laboratory, providing short and efficient routes to a diverse range of known and unknown acenaphtho-annulated linear and angular PAHs, heteroaromatics and five-membered heterocycles in good yields. Thus, benzo- and naphthoannulation of 2 with various allyl and benzyl Grignard reagents afforded substituted fluoranthenes 4a-c and benzo[k]fluoranthene 8, respectively, in good yields. Similarly, the parent benzo[j]fluoranthene 15a and its substituted derivative 16b have been synthesized by base-induced conjugate 1,4-addition of arylacetonitriles to 2, followed by acid-induced cyclization of the conjugate adducts 12a-b to give 13a-b and subsequent further transformations. The adducts obtained by 1,4-addition of anions derived from acetophenone and acenaphthenone were subjected to heterocyclization in the presence of ammonium acetate to give 8-arylacenaphtho[1,2-b]pyridines 18a-b and bis(acenaphtho)-annulated pyridine 20. Heterocyclization of 2 with bifunctional nucleophiles such as 2-picolyllithium and guanidinium nitrate afforded the corresponding acenaphtho[1,2-b]quinolizinium salt 23 and acenaphtho[1,2-d]pyrimidine 24, respectively, in high yields. Finally, acenaphtho[1,2-c]-fused five-membered heterocycles such as 7-(methylthio)acenaphtho[1,2-c]thiophene (25), 7-(methylthio)acenaphtho[1,2-c]furan (27) and 7-(methylthio)acenaphtho[1,2-c] pyrrole-2-carboxylic acid (30) were obtained in good yields by subjection of 2 to Simmons-Smith reaction conditions or by treatment with dimethylsulfonium methylide or glycinate dianion. Some of these newly synthesized PAHs or fused heterocycles were subjected to Raney Ni desulfurization to furnish sulfurfree compounds. Wiley-VCH Verlag GmbH & Co. KGaA, 69451 Weinheim, Germany, 2005.

Relationship between pressure fluctuations and generation of organic pollutants with different particle size distributions in a fluidized bed incinerator

Lin, Chiou-Liang,Wey, Ming-Yen,Cheng, Han-Tsung

, p. 911 - 922 (2007/10/03)

The hydrodynamic behaviors of fluidization perhaps significantly influence the uniformity of fluidization in fluidized bed incinerator. Good uniformity of fluidization expressed the air across uniformly through the bed and the particles being distributed well in the fluid stream. The aggregates, flocs and channels of particles do not happen during fluidization. The Good uniformity will maintain high heat and mass distribution to improve reaction efficiency. These parameters include the height of static bed, gas velocity, mixing and distribution of bed particle, which have rarely been studied in previous investigations. Consequently, this study examines how the hydrodynamic parameters affect the generation of organic pollutants (BTEXs and PAHs) during incineration. The statistical and power spectral analysis of the measured pressure fluctuation during incineration are used to elucidate the relationship between behaviors of fluidization and generation of pollutants during incineration. Experimental results show the organic concentration does not increase with uniformity of fluidization decreasing. The reason may be the explosion of the gas and the consequent thermal shock destroy the coalescent bubbles to form small bubbles again and enhance the efficiency of transfer of oxygen to increase combustion efficiency. Additionally, the mean amplitude and fluidized index of pressure fluctuation similarly vary with the concentration of organic pollutants. These two indices can be used to assess the efficiency of combustion. The four particle size distributions could be divided into two groups by statistical analysis. The Gaussian and narrow distributions belong to one group and the binary and flat the other. The organic concentration of the Gaussian and narrow distributions are lower than that of the other distributions. Consequently, the bed materials should maintain narrow or Gaussian distributions to maintain a good combustion efficiency during incineration.

Post a RFQ

Enter 15 to 2000 letters.Word count: 0 letters

Attach files(File Format: Jpeg, Jpg, Gif, Png, PDF, PPT, Zip, Rar,Word or Excel Maximum File Size: 3MB)

1 Customer Service

What can I do for you?
Get Best Price

Get Best Price for 207-08-9