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Benzo[e]pyrene, an orthoand peri-fused polycyclic arene consisting of five fused benzene rings, is a crystalline, solid substance that appears as prisms or plates. It is sensitive to ultraviolet light and may degrade into diones. Listed as a Group 3 carcinogen by the International Agency for Research on Cancer (IARC), Benzo[e]pyrene is a yellow to yellow-green crystalline powder.

192-97-2

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192-97-2 Usage

Uses

Used in Immunology Studies:
Benzo[e]pyrene is utilized in the study of immune suppressive activity on antibody response to DNP-Ficoll and sheep erythrocytes. This application aids in understanding the compound's impact on the immune system and its potential effects on various biological processes.
Used in Environmental Chemistry:
The "dispersive liquid-liquid micro extraction" technique employs Benzo[e]pyrene for extracting organic compounds from water samples. This application highlights its importance in environmental chemistry, particularly in the analysis and monitoring of water quality and contamination.

Air & Water Reactions

Insoluble in water.

Reactivity Profile

BENZO[E]PYRENE may be sensitive to prolonged exposure to light.

Health Hazard

There is very little information available onits toxicity. The oral toxicity is expected to below. Its carcinogenic potential is lower thanthat of benz[a]pyrene. Animal studies gaveinconclusive results. Oral administration mayproduce tumors in the stomach. However, theevidence of carcinogenicity of Benzo[e]pyrenein animals is inadequate. Benz[e]pyrene isa mutagen, testing positive to the histidinereversion–Ames test and in vitro unscheduled DNA synthesis (UDS)–human fibroblast.

Fire Hazard

Flash point data for BENZO[E]PYRENE are not available. BENZO[E]PYRENE is probably combustible.

Safety Profile

For occupational chemicalanalysis use NIOSH: Polynuclear Aromatic Hydrocarbons(HPLC), 5506; (GC), 5515.

Source

The concentration of benzo[e]pyrene in coal tar and the maximum concentration reported in groundwater at a mid-Atlantic coal tar site were 3,700 and 0.0034 mg/L, respectively (Mackay and Gschwend, 2001). Detected in 8 diesel fuels at concentrations ranging from 0.047 to 2.1 mg/L with a mean value of 0.113 mg/L (Westerholm and Li, 1994). Identified in Kuwait and South Louisiana crude oils at concentrations of 0.5 and 2.5 ppm, respectively (Pancirov and Brown, 1975). Benzo[e]pyrene is produced from the combustion of tobacco and petroleum fuels. It also occurs in low octane gasoline (0.18–0.87 mg/kg), high octane gasoline (0.45–1.82 mg/kg), used motor oil (92.2–278.4 mg/kg), asphalt (≤0.0052 wt %), coal tar pitch (≤0.70 wt %), cigarette smoke (3 μg/1,000 cigarettes), and gasoline exhaust (quoted, Verschueren, 1983). Lehmann et al. (1984) reported a benzo[e]pyrene concentration of 0.02 mg/g in a commercial anthracene oil. 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[e]pyrene were 0.459 mg/kg of pine burned, 0.231 mg/kg of oak burned, and 0.212 mg/kg of eucalyptus burned. Particle-phase tailpipe emission rates from gasoline-powered automobiles with and without catalytic converters were 0.015 and 38.2 μg/km, respectively (Schauer et al., 2002).

Environmental fate

Photolytic. Schwarz and Wasik (1976) reported a fluorescence quantum yield of ≈ 0.3 for benzo[e]pyrene in water. Chemical/Physical. Benzo[e]pyrene will not hydrolyze because it has no hydrolyzable functional group.

Purification Methods

Purify it by passage through an Al2O3 column (Woelm, basic, activity I) and elute with *C6H6 and recrystallise from 2 volumes of EtOH/*C6H6 (4:1). It forms colourless or light yellow prisms or needles. [Campbell J Chem Soc 3659 1954, Buchta & Kr.ger Justus Liebigs Ann Chem 705 190 1967.] The 1,3,5-trinitrobenzene complex has m 253-254o (orange needles from EtOH), the picrate prepared by mixing 20mg in 1mL of *C6H6 with 20mg of picric acid in 2mL *C6H6, collecting the deep red crystals, and recrystallising from *C6H6 has m 228-229o [NMR: Cobb & Memory J Chem Phys 47 2020 1967]. [Beilstein 5 III 2520, 5 I V 2689.] CARCINOGEN.

Check Digit Verification of cas no

The CAS Registry Mumber 192-97-2 includes 6 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 3 digits, 1,9 and 2 respectively; the second part has 2 digits, 9 and 7 respectively.
Calculate Digit Verification of CAS Registry Number 192-97:
(5*1)+(4*9)+(3*2)+(2*9)+(1*7)=72
72 % 10 = 2
So 192-97-2 is a valid CAS Registry Number.
InChI:InChI=1/C20H12/c1-2-8-16-15(7-1)17-9-3-5-13-11-12-14-6-4-10-18(16)20(14)19(13)17/h1-12H

192-97-2 Well-known Company Product Price

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  • Supelco

  • (442475)  Benzo[e]pyrene  analytical standard

  • 192-97-2

  • 000000000000442475

  • 1,423.89CNY

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  • Sigma-Aldrich

  • (36962)  Benzo[e]pyrenesolution  100 μg/mL in cyclohexane, analytical standard

  • 192-97-2

  • 36962-2ML

  • 629.46CNY

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  • Aldrich

  • (B10102)  Benzo[e]pyrene  98%

  • 192-97-2

  • B10102-25MG

  • 1,411.02CNY

  • Detail
  • Aldrich

  • (B10102)  Benzo[e]pyrene  98%

  • 192-97-2

  • B10102-100MG

  • 3,608.28CNY

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192-97-2SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 16, 2017

Revision Date: Aug 16, 2017

1.Identification

1.1 GHS Product identifier

Product name benzo[e]pyrene

1.2 Other means of identification

Product number -
Other names 4,5-Benzpyrene

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:192-97-2 SDS

192-97-2Synthetic route

9-Hydroxy-1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene
68151-09-7

9-Hydroxy-1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
palladium on activated charcoal at 300 - 320℃; for 2h;86%
cis-8b,9,10,11,12,12a-hexahydrobenzopyrene
86439-17-0

cis-8b,9,10,11,12,12a-hexahydrobenzopyrene

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone In toluene for 6h; Heating;78%
With 2,3-dicyano-5,6-dichloro-p-benzoquinone In toluene for 6h; Heating;56%
exo-4,5-dihydrobenzopyreno-2',3':4,5-norbornane
121617-90-1

exo-4,5-dihydrobenzopyreno-2',3':4,5-norbornane

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
In gas under 0.01 - 0.05 Torr; sublimation at 150-200 degC, 4 h to a quartz tube of 800 degC;69%
benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone In toluene for 6h; Heating;60%
trans-4,5-Dihydroxy-4,5-divinyl-4,5-dihydropyrene
77320-76-4

trans-4,5-Dihydroxy-4,5-divinyl-4,5-dihydropyrene

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With trichlorophosphate In pyridine for 0.166667h; Heating;52%
3-(4H-cyclopentaphenanthrylidene)-1,5-bis(trimethylsilyl)-1,4-pentadiyne
157729-37-8

3-(4H-cyclopentaphenanthrylidene)-1,5-bis(trimethylsilyl)-1,4-pentadiyne

A

pyrene
129-00-0

pyrene

B

benzo[e]pyrene
192-97-2

benzo[e]pyrene

C

4H-Cyclopenta[def]phenanthrene
203-64-5

4H-Cyclopenta[def]phenanthrene

D

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

cyclopenta[c,d]pyrene

E

benzo[ghi]fluoranthene
203-12-3

benzo[ghi]fluoranthene

F

Coarannulen
5821-51-2

Coarannulen

Conditions
ConditionsYield
With hydrogen In gas at 900℃; Product distribution; electrically heated vertical laboratory tubular furnace;A n/a
B n/a
C n/a
D n/a
E n/a
F 15%
3-(4H-cyclopentaphenanthrylidene)-1,5-bis(trimethylsilyl)-1,4-pentadiyne
157729-37-8

3-(4H-cyclopentaphenanthrylidene)-1,5-bis(trimethylsilyl)-1,4-pentadiyne

A

pyrene
129-00-0

pyrene

B

benzo[e]pyrene
192-97-2

benzo[e]pyrene

C

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

cyclopenta[c,d]pyrene

D

Coarannulen
5821-51-2

Coarannulen

Conditions
ConditionsYield
With hydrogen In gas at 900℃; electrically heated vertical laboratory tubular furnace; Further byproducts given;A n/a
B n/a
C n/a
D 15%
9-Oxo-1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene
68151-08-6

9-Oxo-1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With ethanol; sodium Erhitzen des Reaktionsprodukts mit Selen auf 320-340grad;
6-propyl-benz[de]anthracen-7-one
857580-09-7

6-propyl-benz[de]anthracen-7-one

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With zinc
9,10-dihydroanthracene
613-31-0

9,10-dihydroanthracene

acrolein
107-02-8

acrolein

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With hydrogen fluoride at 3 - 20℃; Destillation des Reaktionsprodukts in Gegenwart von Quecksilber;
With hydrogen fluoride at 3 - 20℃; Destillation des Reaktionsprodukts in Gegenwart von Quecksilber;
7H-benz[d,e]anthracene
199-94-0

7H-benz[d,e]anthracene

1-dimethylamino-3-dimethylimonioprop-1-ene perchlorate

1-dimethylamino-3-dimethylimonioprop-1-ene perchlorate

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With sodium methylate Multistep reaction;
4-phenyl-2,3-phenantrenedicarboxylic acid anhydride
114468-92-7

4-phenyl-2,3-phenantrenedicarboxylic acid anhydride

A

benzo[e]pyrene
192-97-2

benzo[e]pyrene

B

4-phenylphenanthrene
4325-78-4

4-phenylphenanthrene

Conditions
ConditionsYield
With silica gel at 950℃; for 1.4h; Mechanism;A 84 % Chromat.
B 12 % Chromat.
7H-benz[d,e]anthracene
199-94-0

7H-benz[d,e]anthracene

1-dimethylamino-3-dimethylimonioprop-1-ene perchlorate

1-dimethylamino-3-dimethylimonioprop-1-ene perchlorate

A

benzopyrene
50-32-8

benzopyrene

B

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With quinoline; sodium methylate 1.) RT, 3 h, 2.) 180 deg C, 16 h; Yield given. Yields of byproduct given. Title compound not separated from byproducts;
methyl chloride; methane; mixture of

methyl chloride; methane; mixture of

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics;
polyethylene

polyethylene

A

Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

B

benzo[e]pyrene
192-97-2

benzo[e]pyrene

C

PERYLENE
198-55-0

PERYLENE

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

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;
9,10-dihydroanthracene
613-31-0

9,10-dihydroanthracene

acrolein
107-02-8

acrolein

anhydrous HF

anhydrous HF

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
at 5 - 20℃; Erhitzen des Reaktionsprodukts mit Quecksilber;
at 5 - 20℃; Erhitzen des Reaktionsprodukts mit Quecksilber;
(+-)-7-<1.2-dicarboxy-ethyl>-7H-benzanthracene

(+-)-7-<1.2-dicarboxy-ethyl>-7H-benzanthracene

A

benzo[e]pyrene
192-97-2

benzo[e]pyrene

B

PERYLENE
198-55-0

PERYLENE

Conditions
ConditionsYield
With sodium chloride; zinc(II) chloride at 300℃;
potassium-salt of/the/ 4-phenyl-phenanthrene-2,3-dicarboxylic acid

potassium-salt of/the/ 4-phenyl-phenanthrene-2,3-dicarboxylic acid

A

benzo[e]pyrene
192-97-2

benzo[e]pyrene

B

4-phenylphenanthrene
4325-78-4

4-phenylphenanthrene

Conditions
ConditionsYield
With soda lime; copper Erhitzen unter vermindertem Druck;
ethanol
64-17-5

ethanol

9-Oxo-1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene
68151-08-6

9-Oxo-1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene

sodium

sodium

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
Erhitzen des Reaktionsprodukts mit Selen auf 320-340grad;
6-propyl-benz[de]anthracen-7-one
857580-09-7

6-propyl-benz[de]anthracen-7-one

zinc-powder

zinc-powder

benzo[e]pyrene
192-97-2

benzo[e]pyrene

(7H-benz[de]anthracen-7-yl)-succinic acid

(7H-benz[de]anthracen-7-yl)-succinic acid

(E)-3-Ureido-but-2-enoic acid ethyl ester
5435-44-9, 22243-66-9

(E)-3-Ureido-but-2-enoic acid ethyl ester

sodium chloride

sodium chloride

A

benzo[e]pyrene
192-97-2

benzo[e]pyrene

B

PERYLENE
198-55-0

PERYLENE

Conditions
ConditionsYield
at 300℃;
Eucalyptus grandis wood

Eucalyptus grandis wood

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
Decomposition; Formation of xenobiotics; pyrolysis;
wood

wood

A

anthracene
120-12-7

anthracene

B

fluoranthene
206-44-0

fluoranthene

C

benzopyrene
50-32-8

benzopyrene

D

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics; Further byproducts given;
bituminous coal

bituminous coal

A

naphthalene
91-20-3

naphthalene

B

chrysene
218-01-9

chrysene

C

benz[a]anthracene
56-55-3

benz[a]anthracene

D

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With air at 800℃; Oxidation; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
small intercontinental ballistic missile propellant

small intercontinental ballistic missile propellant

A

pyrene
129-00-0

pyrene

B

fluoranthene
206-44-0

fluoranthene

C

benzo[e]pyrene
192-97-2

benzo[e]pyrene

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

Conditions
ConditionsYield
With oxygen at 1023.85 - 1161.85℃; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
standard missile deload propellant

standard missile deload propellant

A

pyrene
129-00-0

pyrene

B

benzo[e]acephenanthrylene
205-99-2

benzo[e]acephenanthrylene

C

fluoranthene
206-44-0

fluoranthene

D

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With oxygen at 1036.85 - 1162.85℃; Formation of xenobiotics; Further byproducts given. Title compound not separated from byproducts;
Dimethyl ether
115-10-6

Dimethyl ether

A

pyrene
129-00-0

pyrene

B

Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

C

benzo[e]pyrene
192-97-2

benzo[e]pyrene

D

4H-Cyclopenta[def]phenanthrene
203-64-5

4H-Cyclopenta[def]phenanthrene

Conditions
ConditionsYield
With air at 840℃; under 19501.6 Torr; Formation of xenobiotics; high pressure combustion; Further byproducts given. Title compound not separated from byproducts;
compressed natural gas

compressed natural gas

A

pyrene
129-00-0

pyrene

B

naphthalene
91-20-3

naphthalene

C

Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

D

benzo[e]pyrene
192-97-2

benzo[e]pyrene

Conditions
ConditionsYield
With air at 880℃; under 18001.4 Torr; Formation of xenobiotics; high pressure combustion; Further byproducts given. Title compound not separated from byproducts;
benzo[e]pyrene
192-97-2

benzo[e]pyrene

3-Bromobenzopyrene
26105-52-2

3-Bromobenzopyrene

Conditions
ConditionsYield
With benzyltrimethylazanium tribroman-2-uide; zinc(II) chloride In chloroform at 20℃; for 3h;96%
With benzyltrimethylazanium tribroman-2-uide; zinc(II) chloride In chloroform at 20℃; for 3h;96%
benzo[e]pyrene
192-97-2

benzo[e]pyrene

benzopyrene-4,5-dione
66788-08-7

benzopyrene-4,5-dione

Conditions
ConditionsYield
With tert.-butylhydroperoxide; Ru(2,4,13,15-tetraphenyl-1,5,12,16-tetraaza-tricyclo[14.2.2.06,11]eicosa-4,6(11),7,9,12-pentaene)Cl2 In acetonitrile for 6h; Reagent/catalyst; Irradiation;80%
With sodium periodate; rhodium(III) chloride hydrate In dichloromethane; water; acetonitrile at 30 - 40℃;38%
Multi-step reaction with 2 steps
1: (i) OsO4, Py, (ii) aq. NaHSO3, Py
2: DDQ
View Scheme
benzo[e]pyrene
192-97-2

benzo[e]pyrene

3,6-Dibromobenzopyrene
77508-03-3

3,6-Dibromobenzopyrene

Conditions
ConditionsYield
With bromine In chlorobenzene for 0.25h; Ambient temperature;78%
With bromine In chlorobenzene
2,4,6-tri(4-pyridyl)-1,3,5-triazine
42333-78-8

2,4,6-tri(4-pyridyl)-1,3,5-triazine

[Ru2(η6-p-cymene)2(C6H2O4)Cl2]
1039768-31-4

[Ru2(η6-p-cymene)2(C6H2O4)Cl2]

benzo[e]pyrene
192-97-2

benzo[e]pyrene

silver trifluoromethanesulfonate
2923-28-6

silver trifluoromethanesulfonate

benzo[e]pyrene*[Ru6(p-cymene)6(2,4,6-tris(4-pyridyl)-1,3,5-triazine)2(2,5-dioxy-1,4-benzoquinonato)3](O3SCF3)6

benzo[e]pyrene*[Ru6(p-cymene)6(2,4,6-tris(4-pyridyl)-1,3,5-triazine)2(2,5-dioxy-1,4-benzoquinonato)3](O3SCF3)6

Conditions
ConditionsYield
In methanol byproducts: AgCl; a mixt. of complex and Ag-salt in methanol was stirred at room temp. for2 h, filtered, triazine-compound and aromatic molecule were added, the mixt. was stirred at room temp. for 24 h; the solvent was removed under vac., the residue was taken up in CH2Cl2, filtered, concd., diethyl ether was added; elem. anal.;68%
silver tetrafluoroborate
14104-20-2

silver tetrafluoroborate

[ruthenium(II)(η6-1-methyl-4-isopropyl-benzene)(chloride)(μ-chloride)]2
52462-29-0

[ruthenium(II)(η6-1-methyl-4-isopropyl-benzene)(chloride)(μ-chloride)]2

benzo[e]pyrene
192-97-2

benzo[e]pyrene

[(η6-4,5-benzopyrene)(η6-4-(methylisopropyl)benzene)ruthenium(II)](BF4)2

[(η6-4,5-benzopyrene)(η6-4-(methylisopropyl)benzene)ruthenium(II)](BF4)2

Conditions
ConditionsYield
In dichloromethane; acetone byproducts: AgCl; reaction under N2: addn. of AgBF4 to a soln. of Ru-complex in acetone, stirring for 15 min at room temp., filtn. to remove AgCl, evapn. of solvent under vac., addn. of CH2Cl2 along with the ligand, refluxing for 48 h; filtn., washing with CH2Cl2 and Et2O, elem. anal.;56%
phthalic anhydride
85-44-9

phthalic anhydride

benzo[e]pyrene
192-97-2

benzo[e]pyrene

5-(o-Carboxybenzoyl)-1,2-benzopyren

5-(o-Carboxybenzoyl)-1,2-benzopyren

Conditions
ConditionsYield
With aluminium trichloride In benzene
benzo[e]pyrene
192-97-2

benzo[e]pyrene

3,5,8,10-Tetrachlo-1,2-benzpyren
95430-01-6

3,5,8,10-Tetrachlo-1,2-benzpyren

Conditions
ConditionsYield
With chlorine
benzo[e]pyrene
192-97-2

benzo[e]pyrene

1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene
92387-50-3

1,2,3,6,7,8,9,10,11,12-decahydrobenzopyrene

Conditions
ConditionsYield
With sodium In pentan-1-ol
benzo[e]pyrene
192-97-2

benzo[e]pyrene

6-Brom-benzopyren

6-Brom-benzopyren

Conditions
ConditionsYield
With o-tetrachloroquinone; hydrogen bromide
benzo[e]pyrene
192-97-2

benzo[e]pyrene

ortho-toluoyl chloride
933-88-0

ortho-toluoyl chloride

5-

5-

Conditions
ConditionsYield
With aluminium trichloride In dichloromethane
benzo[e]pyrene
192-97-2

benzo[e]pyrene

cis-4,5-Dihydroxy-4,5-dihydrobenzopyrene
24909-10-2

cis-4,5-Dihydroxy-4,5-dihydrobenzopyrene

Conditions
ConditionsYield
(i) OsO4, Py, (ii) aq. NaHSO3, Py; Multistep reaction;
With osmium(VIII) oxide In pyridine; benzene for 120h; in the dark;
benzo[e]pyrene
192-97-2

benzo[e]pyrene

A

3,6-Dibromobenzopyrene
77508-03-3

3,6-Dibromobenzopyrene

B

3-Bromobenzopyrene
26105-52-2

3-Bromobenzopyrene

Conditions
ConditionsYield
With bromine In chlorobenzene for 0.5h; Product distribution; Ambient temperature; various amounts of bromine and times of the reaction;
With bromine In chlorobenzene for 0.5h; Ambient temperature; Yield given. Yields of byproduct given;
benzo[e]pyrene
192-97-2

benzo[e]pyrene

A

1-nitrobenzopyrene

1-nitrobenzopyrene

B

1-nitrobenzopyrene

1-nitrobenzopyrene

Conditions
ConditionsYield
With nitric acid at 0℃; for 90h; Yield given. Yields of byproduct given;
benzo[e]pyrene
192-97-2

benzo[e]pyrene

A

1-fluoro-benzo[e]pyrene

1-fluoro-benzo[e]pyrene

B

4-fluoro-benzo[e]pyrene

4-fluoro-benzo[e]pyrene

C

3-fluoro-benzo[e]pyrene

3-fluoro-benzo[e]pyrene

Conditions
ConditionsYield
With N-fluoro-2,4-dinitroimidazole In 1,2-dichloro-ethane for 72h; Heating; Yield given; Yields of byproduct given. Title compound not separated from byproducts;

192-97-2Related news

Reduced cytochrome P4501A activity and recovery from oxidative stress during subchronic benzo[a]pyrene and benzo[e]pyrene treatment of rainbow trout09/30/2019

This study assessed the role of aryl hydrocarbon receptor (AHR) affinity, and cytochrome P4501A (CYP1A) protein and activity in polyaromatic hydrocarbon (PAH)-induced oxidative stress. In the 1–100nM concentration range benzo[a]pyrene (BaP) but not benzo[e]pyrene (BeP) competitively displaced 2...detailed

192-97-2Relevant academic research and scientific papers

Novel Annelation Reaction: Synthesis of Polycyclic Hydrocarbons from o-Quinones

Sukumaran, Kutikat B.,Harvey, Ronald G.

, p. 2740 - 2745 (1981)

A novel general synthesis of polycyclic aromatic ring systems involving initial reaction of polycyclic o-quinone with lithium acetylide, reduction of the resulting diacetylenic diol with LiAlH4 to the corresponding divinyl diol, and finally cyclization and dehydration with HI or POCl3 to a polyarene having one more aromatic ring is reported.Syntheses of triphenylene, dibenzanthracene, benzopyrene, and benzochrysene by this means from phenanthrene-9,10-dione, benzanthracene-5,6-dione, pyrene-4,5-dione, and chrysene-5,6-dione, respectively, are described.Yields are high (94-97percent) in the initial two steps and good (52-74percent) in the final stage.The divinyl diol intermediates may be generated directly, though in lower yield, via direct reaction of the quinones with vinylmagnesium bromide or vinyllithium reagents.Various related reactions are also explored, and evidence concerning the stereochemistries of the intermediates and the mechanisms of these reactions is discussed.

Spectrometry and reactivity of benzanthrenyl and 1-hydroperylenyl anions

Van Dijk, Joost T. M.,Van De Panne, Berit J.,Bleeker, Annemarie C.,Lugtenburg, Johan,Cornelisse, Jan

, p. 2647 - 2662 (1996)

Charge distribution and reactivity of benzanthrenyl (1-) and 1-methyl-1-hydroperylenyl anion (2-) are examined by means of semiempirical calculations, NMR spectroscopy and reactions with electrophiles. Highest charge density and reactivity are located at position 7 of 1- and the comparable position 12b of 2-. A small degree of reactivity is located at positions 4 and 6 of 1-, as shown by reactions. Generally, a good correlation between calculated charge distribution and charge distribution obtained from 13C NMR is observed.

REINVESTIGATION OF THE JUTZ SYNTHESIS OF BENZOPYRENE AND BENZOPYRENE DERIVATES FROM BENZANTHRENE

Lee, Hongmee,Harvey, Ronald G.

, p. 995 - 996 (1981)

Base-catalyzed reactions of benzanthrene with "vinamidium salts" (2a-c) followed by thermal electrocyclic ring closure are regiospecific affording only benzopyrene derivates, contrary to previous claims.

Emission factors for carbonaceous particles and polycyclic aromatic hydrocarbons from residential coal combustion in China

Chen, Yingjun,Sheng, Guoying,Bi, Xinhui,Feng, Yanli,Mai, Bixian,Fu, Jiamo

, p. 1861 - 1867 (2008/12/21)

Emission factors of carbonaceous particles, including black carbon (BC) and organic carbon (OC), and polycyclic aromatic hydrocarbons (PAHs) were determined for five coals, which ranged in maturity from sub-bituminous to anthracite. They were burned in the form of honeycomb briquettes in a residential coalstove, one of the most common fuel/stove combinations in China. Smoke samples were taken through dilution sampling equipment, with a high volume sampler that could simultaneously collect emissions in both particulate and gaseous phases, and a cascade impactor that could segregate particles into six fractions. Particulate BC and OC were analyzed by a thermal-optical method, and PAHs in emissions of both phases were analyzed by GC-MS. Burning of bituminous coals produced the highest emission factors of particulate matter (12.91 g/kg), BC (0.28 g/kg), OC (7.82 g/kg), and 20 PAHs (210.6 mg/kg) on the basis of burned dry ash-free (daf) coal, while the anthracite honeycomb-briquette was the cleanest household coal fuel. The size-segregated results show that more than 94% of the particles were submicron, and calculated mass median aerodynamic diameters (MMAD) of all particles were under 0.3 μm. Based on the coal consumption in the residential sector of China, 290.24 Gg (gigagrams) of particulate matter, 5.36 Gg of BC, 170.33 Gg of OC, and 4.72 Gg of 20 PAHs mass were emitted annually from household honeycomb-briquette burning during 2000. Anthracite coal should be selected preferentially and more advanced burning conditions should be applied in domestic combustion, from the viewpoint of both climate change and adverse health effects.

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.

Semivolatile and volatile compounds in combustion of polyethylene

Font, Rafael,Aracil, Ignacio,Fullana, Andrés,Conesa, Juan A.

, p. 615 - 627 (2007/10/03)

The evolution of semivolatile and volatile compounds in the combustion of polyethylene (PE) was studied at different operating conditions in a horizontal quartz reactor. Four combustion runs at 500 and 850°C with two different sample mass/air flow ratios and two pyrolytic runs at the same temperatures were carried out. Thermal behavior of different compounds was analyzed and the data obtained were compared with those of literature. It was observed that α,ω-olefins, α-olefins and n-paraffins were formed from the pyrolytic decomposition at low temperatures. On the other hand, oxygenated compounds such as aldehydes were also formed in the presence of oxygen. High yields were obtained of carbon oxides and light hydrocarbons, too. At high temperatures, the formation of polycyclic aromatic hydrocarbons (PAHs) took place. These compounds are harmful and their presence in the combustion processes is related with the evolution of pyrolytic puffs inside the combustion chamber with a poor mixture of semivolatile compounds evolved with oxygen. Altogether, the yields of more than 200 compounds were determined. The collection of the semivolatile compounds was carried out with XAD-2 adsorbent and were analyzed by GC-MS, whereas volatile compounds and gases were collected in a Tedlar bag and analyzed by GC with thermal conductivity and flame ionization detectors.

Semi-volatile and particulate emissions from the combustion of alternative diesel fuels

Sidhu, Sukh,Graham, John,Striebich, Richard

, p. 681 - 690 (2007/10/03)

Motor vehicle emissions are a major anthropogenic source of air pollution and contribute to the deterioration of urban air quality. In this paper, we report results of a laboratory investigation of particle formation from four different alternative diesel fuels, namely, compressed natural gas (CNG), dimethyl ether (DME), biodiesel, and diesel, under fuelrich conditions in the temperature range of 800-1200°C at pressures of approximately 24 atm. A single pulse shock tube was used to simulate compression ignition (CI) combustion conditions. Gaseous fuels (CNG and DME) were exposed premixed in air while liquid fuels (diesel and biodiesel) were injected using a high-pressure liquid injector. The results of surface analysis using a scanning electron microscope showed that the particles formed from combustion of all four of the above-mentioned fuels had a mean diameter less than 0.1 μm. From results of gravimetric analysis and fuel injection size it was found that under the test conditions described above the relative particulate yields from CNG, DME, biodiesel, and diesel were 0.30%, 0.026%, 0.52%, and 0.51%, respectively. Chemical analysis of particles showed that DME combustion particles had the highest soluble organic fraction (SOF) at 71%, followed by biodiesel (66%), CNG (38%) and diesel (20%). This illustrates that in case of both gaseous and liquid fuels, oxygenated fuels have a higher SOF than non-oxygenated fuels. Motor vehicle emissions are a major anthropogenic source of air pollution and contribute to the deterioration of urban air quality. In this paper, we report results of a laboratory investigation of particle formation from four different alternative diesel fuels, namely, compressed natural gas (CNG), dimethyl ether (DME), biodiesel, and diesel, under fuelrich conditions in the temperature range of 800-1200°C at pressures of approximately 24 atm. A single pulse shock tube was used to simulate compression ignition (CI) combustion conditions. Gaseous fuels (CNG and DME) were exposed premixed in air while liquid fuels (diesel and biodiesel) were injected using a high-pressure liquid injector. The results of surface analysis using a scanning electron microscope showed that the particles formed from combustion of all four of the above-mentioned fuels had a mean diameter less than 0.1 μm. From results of gravimetric analysis and fuel injection size it was found that under the test conditions described above the relative particulate yields from CNG, DME, biodiesel, and diesel were 0.30%, 0.026%, 0.52%, and 0.51%, respectively. Chemical analysis of particles showed that DME combustion particles had the highest soluble organic fraction (SOF) at 71%, followed by biodiesel (66%), CNG (38%) and diesel (20%). This illustrates that in case of both gaseous and liquid fuels, oxygenated fuels have a higher SOF than non-oxygenated fuels.

Transient puffs of trace organic emissions from a batch-fed waste propellant incinerator

Hart, John R.

, p. 559 - 569 (2007/10/03)

Emissions data have been obtained from a waste propellant incinerator. The incinerator is a dual fixed hearth, controlled air incinerator equipped with acid gas and particulate scrubbing. Puffing has been evident in this waste propellant incinerator by spikes in the CO concentration. Transient puffs of organics may travel down the combustion chambers and lead to stack emissions. The major conclusions from this study are that (1) transient puffs are formed due to the semi-batch feed nature of the combustion process (causing a local oxygen deficiency) and high water content of the desensitized propellant; (2) in batch-fed combustors, puffs can contribute to most of the organic emissions (which are relatively low) measured with US EPA sampling and analytical methods; (3) it is estimated that batch-fed combustion contributes up to 7-18 times more emissions than steady-state combustion will generate; (4) by applying dispersion analyses to determine the amount of oxygen deficiency in the flame zone, the combustion zone concentration of CO during batch-fed operation could be as high as 160,000 ppm, compared to a measured peak stack concentration of 1200 ppm CO; and (5) an organic sample is collected and averaged over at least a 2-h period that smooths out the transient peaks of organics emissions during batch-fed operation. For emissions that are associated with long-term potential health impacts, this is an appropriate sampling method. However, if a compound has a short-term potential health impact, it may be important to measure the time-resolved emissions of the compound.

Influence of combustion conditions on the PCDD/F-, PCB-, PCBz- and PAH- concentrations in the post-combustion chamber of a waste incineration pilot plant

Blumenstock,Zimmermann,Schramm,Kettrup

, p. 987 - 993 (2007/10/03)

Experiments at a pilot scale waste incinerator (0.5 MW thermal power) showed that the conditions in the postcombustion chamber (650-900°C) are strongly influencing the formation of chlorinated and non-chlorinated aromatics. Non-optimal combustion conditions resulted in increased concentrations of mono- to trichlorinated dibenzo-p-dioxins (PCDD), dibenzofurans (PCDF) and polycyclic aromatic hydrocarbons (PAH), while chlorinated benzenes (PCBz), polychlorinated biphenyls (PCB) and the higher chlorinated PCDD/F are only weakly affected or even decrease. The changes in concentration of the compounds investigated over a time span of hours gave hints on 'memory effects' in this combustion zone. For mono- and dichlorinated benzenes, a high correlation (r2 = 0.80) with the international toxicity equivalent (I-TEQ) value of PCDD/F was observed. As recently has been demonstrated, this correlation can be utilized for an indirect on-line measurement of the I-TEQ by a novel laser mass spectrometric technique (REMPI-TOFMS). (C) 2000 Elsevier Science Ltd.

Investigation of polycyclic aromatic hydrocarbons in fly ash from fluidized bed combustion systems

Liu, Kunlei,Xie, Wei,Zhao, Zheng-Bao,Pan, Wei-Ping,Riley, John T.

, p. 2273 - 2279 (2007/10/03)

A laboratory scale fluidized bed reactor and a bench scale 0.1 MW(th) fluidized bed combustor were used to study the effect of operating conditions on the formation of Polycyclic Aromatic Hydrocarbons (PAHs) in fly ash from fluidized bed combustion systems. A high volatile bituminous coal was chosen to investigate PAH emissions during the entire pyrolysis to oxygen-rich combustion process. During the experiments, the fluidized bed reactor was operated at temperatures between 700°C and 900°C, while the excess air ratio was varied from 0 to 1.3. An extraction and GC/MS analysis of PAHs was used in this study. Approximately 40 different PAHs were identified during the tests, of which only a few are specified by the U.S. EPA. The experimental results indicate the majority of the PAHs in the solid phase (bed and fly ash) are derived from the breakdown reactions during the processes of combustion and/or pyrolysis in a Fluidized Bed Combustion (FBC) system, although FBC systems have an efficient solid-gas mixing process and relatively long residence time. The total amount of PAHs in the fly ash was much higher than that in the raw coal and in the gas phase. Three-and four- ring aromatic compounds were the major PAHs from pyrolysis conditions, while naphthalene (two-rings) is the dominant compound in bed ash collected from oxygen-rich combustion conditions. Only naphthalene was detected in the bed ash in the FBC system. High-speed secondary air (air staging) injected into the freeboard of the FBC system is an effective method for minimizing PAH emissions, along with the other benefits including minimizing NO(x) and SO(x) emissions. A laboratory scale fluidized bed reactor and a bench scale 0.1 MWth fluidized bed combustor were used to study the effect of operating conditions on the formation of Polycyclic Aromatic Hydrocarbons (PAHs) in fly ash from fluidized bed combustion systems. A high volatile bituminous coal was chosen to investigate PAH emissions during the entire pyrolysis to oxygen-rich combustion process. During the experiments, the fluidized bed reactor was operated at temperatures between 700°C and 900°C, while the excess air ratio was varied from 0 to 1.3. An extraction and GC/MS analysis of PAHs was used in this study. Approximately 40 different PAHs were identified during the tests, of which only a few are specified by the U.S. EPA. The experimental results indicate the majority of the PAHs in the solid phase (bed and fly ash) are derived from the breakdown reactions during the processes of combustion and/or pyrolysis in a Fluidized Bed Combustion (FBC) system, although FBC systems have an efficient solid-gas mixing process and relatively long residence time. The total amount of PAHs in the fly ash was much higher than that in the raw coal and in the gas phase. Three-and four-ring aromatic compounds were the major PAHs from pyrolysis conditions, while naphthalene (two-rings) is the dominant compound in bed ash collected from oxygen-rich combustion conditions. Only naphthalene was detected in the bed ash in the FBC system. High-speed secondary air (air staging) injected into the freeboard of the FBC system is an effective method for minimizing PAH emissions, along with the other benefits including minimizing NOx and SOx emissions.

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