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Indenopyrene, also known as benzo[b]fluoranthene, is a polycyclic aromatic hydrocarbon (PAH) that is commonly found as a byproduct of the incomplete combustion of organic materials such as fossil fuels, tobacco, and wood. Classified as a Group 2B carcinogen by the International Agency for Research on Cancer, it is considered possibly carcinogenic to humans. Indenopyrene has been associated with various health effects, including respiratory issues, DNA damage, and cancer. Recognized as a priority pollutant by the US Environmental Protection Agency, efforts are underway to reduce its emissions and exposure to safeguard human health and the environment.

193-39-5

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193-39-5 Usage

Uses

Indenopyrene does not have direct applications due to its harmful effects on human health and the environment. However, it is important to monitor and control its presence in various industries to minimize its impact. Some areas where its presence is monitored and controlled include:
Used in Environmental Monitoring:
Indenopyrene is used as a marker for the presence of PAHs in environmental samples, such as air, water, and soil. Monitoring its levels helps in assessing the extent of pollution and the effectiveness of pollution control measures.
Used in Industrial Emission Control:
Indenopyrene is used as a target pollutant in the development and implementation of emission control technologies in industries that involve combustion processes, such as power generation, manufacturing, and transportation. Reducing its emissions contributes to the mitigation of air pollution and the associated health risks.
Used in Research and Toxicology Studies:
Indenopyrene serves as a subject of research in toxicology and environmental chemistry to better understand its mechanisms of action, potential health effects, and ways to mitigate its harmful impacts. This research aids in the development of guidelines and regulations for safe exposure levels and the management of PAHs in the environment.

Check Digit Verification of cas no

The CAS Registry Mumber 193-39-5 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 3 respectively; the second part has 2 digits, 3 and 9 respectively.
Calculate Digit Verification of CAS Registry Number 193-39:
(5*1)+(4*9)+(3*3)+(2*3)+(1*9)=65
65 % 10 = 5
So 193-39-5 is a valid CAS Registry Number.
InChI:InChI=1/C22H12/c1-2-7-17-16(6-1)19-12-15-9-8-13-4-3-5-14-10-11-18(22(17)19)21(15)20(13)14/h1-12H

193-39-5 Well-known Company Product Price

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  • Sigma-Aldrich

  • (94377)  Indeno[1,2,3-cd]pyrene  certified reference material, TraceCERT®

  • 193-39-5

  • 94377-10MG

  • 1,117.35CNY

  • Detail
  • Sigma-Aldrich

  • (36947)  Indeno[1,2,3-c,d]pyrenesolution  100 μg/mL in cyclohexane, analytical standard

  • 193-39-5

  • 36947-2ML

  • 629.46CNY

  • Detail
  • Supelco

  • (48669)  Indeno[1,2,3-c,d]pyrenesolution  certified reference material, 200 μg/mL in methanol

  • 193-39-5

  • 000000000000048669

  • 272.61CNY

  • Detail
  • Supelco

  • (48499)  Indeno[1,2,3-cd]pyrene  analytical standard

  • 193-39-5

  • 000000000000048499

  • 1,820.52CNY

  • Detail
  • Cerilliant

  • (ERI-001)  Indeno[1,2,3-cd]pyrene  vial of 25 mg, analytical standard

  • 193-39-5

  • ERI-001-25MG

  • 731.25CNY

  • Detail
  • Cerilliant

  • (SCI-001)  Indeno[1,2,3-cd]pyrene  vial of 1 g, analytical standard

  • 193-39-5

  • SCI-001-1G

  • 9,868.95CNY

  • Detail

193-39-5SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 17, 2017

Revision Date: Aug 17, 2017

1.Identification

1.1 GHS Product identifier

Product name Indeno[1,2,3-cd]pyrene

1.2 Other means of identification

Product number -
Other names 1,10-(o-Phenylene)pyrene

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:193-39-5 SDS

193-39-5Synthetic route

Trifluoro-methanesulfonic acid 2-pyren-1-yl-phenyl ester

Trifluoro-methanesulfonic acid 2-pyren-1-yl-phenyl ester

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

Indeno[1,2,3-cd]pyrene

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 135 - 140℃; for 6h;91%
2-(pyren-1-yl)aniline
102662-21-5

2-(pyren-1-yl)aniline

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With tert.-butylnitrite In acetonitrile at 20℃; for 10h;85%
With sulfuric acid; acetic acid; sodium nitrite anschliessendes Erwaermen mit Kupfer-Pulver;
C22H15N

C22H15N

phenylacetylene
536-74-3

phenylacetylene

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With fac-tris(2-phenylpyridinato-N,C2')iridium(III); tert.-butylnitrite In acetonitrile at 20℃; for 15h; Sealed tube; Irradiation;84%
1-bromo-2-(1-pyrenyl)benzene
377737-93-4

1-bromo-2-(1-pyrenyl)benzene

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With 1,8-diazabicyclo[5.4.0]undec-7-ene; bis-triphenylphosphine-palladium(II) chloride In N,N-dimethyl-formamide at 140℃; for 11h; Inert atmosphere;72%
1-bromopyrene
1714-29-0

1-bromopyrene

(2-bromophenyl)boronic acid
244205-40-1

(2-bromophenyl)boronic acid

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With 1,8-diazabicyclo[5.4.0]undec-7-ene; tricyclohexylphosphine; tris(dibenzylideneacetone)dipalladium (0) In N,N-dimethyl-formamide at 155℃; for 48h;51%
endo-(8bSR,8cSR,12bRS,12aRS)-8b,8c,11,12,12a,12b-hexahydrobenzocyclobuta<1,2-e>pyrene
92681-17-9, 93861-97-3

endo-(8bSR,8cSR,12bRS,12aRS)-8b,8c,11,12,12a,12b-hexahydrobenzocyclobuta<1,2-e>pyrene

A

4-phenylpyrene
7267-88-1

4-phenylpyrene

B

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone In chloroform Heating;A 10%
B 4%
4-phenylpyrene
7267-88-1

4-phenylpyrene

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With aluminium trichloride; sodium chloride at 120℃;
indeno[1,2,3-cd]pyrene-11,12-dicarboxylic acid-anhydride
5695-26-1

indeno[1,2,3-cd]pyrene-11,12-dicarboxylic acid-anhydride

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With soda lime
pyrene
129-00-0

pyrene

benzene
71-43-2

benzene

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
at 750℃;
phenanthrene
85-01-8

phenanthrene

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

anthracene
120-12-7

anthracene

Conditions
ConditionsYield
at 850℃; Further byproducts given;
7,8,9,10-tetrahydroindeno[1,2,3-cd]pyrene
112312-98-8

7,8,9,10-tetrahydroindeno[1,2,3-cd]pyrene

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone benzene,reflux,30 min.;
C22H18
95676-43-0

C22H18

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone benzene,reflux,30 min.;
2-(pyren-1-yl)cyclohexanone
111189-39-0

2-(pyren-1-yl)cyclohexanone

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With PPA; 2,3-dicyano-5,6-dichloro-p-benzoquinone 1) 100 deg C,2h 2) benzene,reflux,30 min; Yield given. Multistep reaction;
With PPA; 2,3-dicyano-5,6-dichloro-p-benzoquinone 1.) 110 deg C, 2 h, 2.) benzene, reflux, 30 min; Yield given. Multistep reaction;
2-(pyren-1-yl)cyclohexanone
111189-39-0

2-(pyren-1-yl)cyclohexanone

A

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

Indeno[1,2,3-cd]pyrene

B

7,8,9,10-tetrahydroindeno[1,2,3-cd]pyrene
112312-98-8

7,8,9,10-tetrahydroindeno[1,2,3-cd]pyrene

C

C22H18
95676-43-0

C22H18

Conditions
ConditionsYield
With PPA at 100℃; for 2h;
2-(4-pyrenyl)cyclohexanone
111189-40-3

2-(4-pyrenyl)cyclohexanone

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone Multistep reaction;
With PPA; 2,3-dicyano-5,6-dichloro-p-benzoquinone 1.) 110 deg C, 2 h, 2.) benzene, reflux, 30 min; Yield given. Multistep reaction;
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

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

Indeno[1,2,3-cd]pyrene

B

benzopyrene
50-32-8

benzopyrene

C

dibenzo[a,h]anthracene
53-70-3

dibenzo[a,h]anthracene

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics; Further byproducts given;
Eucalyptus grandis wood

Eucalyptus grandis wood

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
Decomposition; Formation of xenobiotics; pyrolysis;
wood

wood

A

pyrene
129-00-0

pyrene

B

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

Indeno[1,2,3-cd]pyrene

C

1,7-dimethylphenanthrene
483-87-4

1,7-dimethylphenanthrene

D

Retene
483-65-8

Retene

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

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

Indeno[1,2,3-cd]pyrene

C

fluoranthene
206-44-0

fluoranthene

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

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

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

Indeno[1,2,3-cd]pyrene

C

fluoranthene
206-44-0

fluoranthene

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

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

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

Indeno[1,2,3-cd]pyrene

B

benzopyrene
50-32-8

benzopyrene

C

dibenzo[a,h]anthracene
53-70-3

dibenzo[a,h]anthracene

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

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

tyre rubber

A

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

Indeno[1,2,3-cd]pyrene

B

benzopyrene
50-32-8

benzopyrene

C

dibenzo[a,h]anthracene
53-70-3

dibenzo[a,h]anthracene

D

Benzo[ghi]perylene
191-24-2

Benzo[ghi]perylene

Conditions
ConditionsYield
With carbon dioxide at 900℃; 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;
polypropylene

polypropylene

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

Indeno[1,2,3-cd]pyrene

Conditions
ConditionsYield
With silica gel Formation of xenobiotics;
Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

C22H11Br
120362-72-3

C22H11Br

Conditions
ConditionsYield
With N-Bromosuccinimide In N,N-dimethyl-formamide at 45℃; for 8h;98%
With bromine In acetic acid for 0.5h;87%
With N-Bromosuccinimide In benzene for 41h; Heating;62%
Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

A

C22H11NO2

C22H11NO2

B

C22H11NO2

C22H11NO2

C

12-Nitroindeno<1,2,3-cd>pyrene

12-Nitroindeno<1,2,3-cd>pyrene

Conditions
ConditionsYield
With dinitrogen tetraoxide In dichloromethane for 0.2h; Ambient temperature; Yield given;A n/a
B n/a
C 91%
With dinitrogen tetraoxide In dichloromethane for 0.2h; Ambient temperature; Yields of byproduct given;A n/a
B n/a
C 91%
Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

acetyl chloride
75-36-5

acetyl chloride

A

8-acetylindeno<1,2,3-cd>pyrene

8-acetylindeno<1,2,3-cd>pyrene

B

12-acetylindeno<1,2,3-cd>pyrene
120362-67-6

12-acetylindeno<1,2,3-cd>pyrene

C

8,12-diacetylindeno<1,2,3-cd>pyrene

8,12-diacetylindeno<1,2,3-cd>pyrene

Conditions
ConditionsYield
With aluminium trichloride In dichloromethane for 0.5h;A n/a
B 62%
C 17%
With aluminium trichloride In dichloromethane at 0℃; for 0.5h;A n/a
B 62%
C 17%
Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

1,2-dihydroindeno<1,2,3-cd>pyrene
120362-68-7

1,2-dihydroindeno<1,2,3-cd>pyrene

Conditions
ConditionsYield
With hydrogen; palladium on activated charcoal In ethyl acetate under 1551.4 Torr; for 70h; Ambient temperature;59%
Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

A

C22H12O

C22H12O

B

C22H12O

C22H12O

C

1-2,6-6a-diepoxyindeno<1,2,3-cd>pyrene

1-2,6-6a-diepoxyindeno<1,2,3-cd>pyrene

Conditions
ConditionsYield
With phosphate buffer; potassium peroxomonosulphate; tetra(n-butyl)ammonium hydrogensulfate; acetone In dichloromethane at 8 - 12℃; for 12h;A 4%
B 33%
C 3%
Indeno[1,2,3-cd]pyrene
193-39-5

Indeno[1,2,3-cd]pyrene

[1,4]naphthoquinone
130-15-4

[1,4]naphthoquinone

indeno[1,2,3-de]naphtho[2,1,8-qra]naphthacene-5,16-dione
122542-61-4

indeno[1,2,3-de]naphtho[2,1,8-qra]naphthacene-5,16-dione

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

Indeno[1,2,3-cd]pyrene

cis-1,2-dihydro-1,2-dihydroxyindeno<1,2,3-cd>pyrene
102420-54-2

cis-1,2-dihydro-1,2-dihydroxyindeno<1,2,3-cd>pyrene

Conditions
ConditionsYield
With osmium(VIII) oxide In pyridine; benzene for 504h; Ambient temperature; Yield given;

193-39-5Relevant academic research and scientific papers

The 2?s + 2?s Photocycloadditions of Triplet Pyrene to Cyclohexa-1,3-diene

Kimura, Masaru,Nukada, Kastumi,Satake, Kyosuke,Morosawa, Shiro,Tamagake, Keiestu

, p. 1431 - 1433 (1984)

exo-(8bSR,8cSR,12bRS,12aSR)-8b,8c,11,12,12a,12b-Hexahydrobenzocyclobutapyrene and endo-(8bSR,8cSR,12bRS,12aRS)-8b,8c,11,12,12a,12b-hexahydrobenzocyclobutapyrene have been isolated; this is the first example of a 2?s + 2?s photocycloaddition between cyclohexa-1,3-diene and 3pyrene.

Extended Study of Visible-Light-Induced Photocatalytic [4 + 2] Benzannulation: Synthesis of Polycyclic (Hetero)Aromatics

Chatterjee, Tanmay,Lee, Da Seul,Cho, Eun Jin

, p. 4369 - 4378 (2017/04/28)

Herein we report an extended study of [4 + 2] benzannulation reactions of 2-(hetero)aryl-substituted anilines with alkynes by visible light photocatalysis. The method requires the use of tBuONO as a diazotizing agent and 0.3 mol % of fac-Ir(ppy)3 as a photocatalyst at room temperature. The reaction proceeded in a chemo- and regioselective manner with high functional group tolerance under mild conditions allowing the preparation of a wide variety of polycyclic (hetero)aromatic compounds, including phenanthrenes, in moderate to high yields. This procedure is amenable to gram-scale synthesis of 9-phenylphenanthrene.

Synthesis of cyclopenta-fused polycyclic aromatic hydrocarbons utilizing aryl-substituted anilines

Choi, Yeojin,Chatterjee, Tanmay,Kim, Jun,Kim, Jun Soo,Cho, Eun Jin

, p. 6804 - 6810 (2016/07/23)

Cyclopenta-fused polycyclic aromatic hydrocarbons (CP-PAHs), potentially electronically and biologically highly active materials, were synthesized from readily available 2-aryl-substituted anilines. Reactions occur under extremely mild, room temperature conditions using tBuONO as the sole reagent. The use of a nitrite source generates a reactive diazonium intermediate in situ that then reacts with a tethered polycyclic aromatic moiety by intramolecular aromatic substitution. This protocol could be presented as one of the simplest methods to access CP-PAHs.

INDENOPYRENE COMPOUND, ORGANIC THIN FILM SOLAR CELL MATERIAL USING THE SAME, AND ORGANIC THIN FILM SOLAR CELL

-

, (2011/05/08)

A specified indenopyrene compound containing a disubstituted amino group substituted with a group having a carbon number of from 1 to 40, which is a useful indenopyrene compound as an organic electronics material, and in particular, an indenopyrene compound which when used for organic thin film solar cells, displays a photoelectric conversion characteristic with high efficiency, is provided.

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.

Oligoindenopyrenes: A new class of polycyclic aromatics

Wegner, Hermann A.,Reisch, Helge,Rauch, Karsten,Demeter, Attila,Zachariasse, Klaas A.,De Meijere, Armin,Scott, Lawrence T.

, p. 9080 - 9087 (2007/10/03)

(Graph Presented) A new class of polycyclic aromatic hydrocarbons - oligoindenopyrenes - has been synthesized featuring a Pd-catalyzed Suzuki - Heck coupling cascade. The oligoindenopyrenes are robust, highly colored substructures of C70 and have properties that might prove useful in new organic materials or devices. After excitation, the tetraindenopyrene derivative 3d undergoes efficient deactivation (99%) by internal conversion to the ground state. The small fluorescence quantum yield (0.004) is in accordance with the short (0.6 ns) fluorescence decay time.

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.

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.

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.

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