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Benzo[a]pyrene, also known as BaP, is a potent mutagen and carcinogen belonging to the class of polycyclic aromatic hydrocarbons (PAHs). It is an odorless, yellow substance that can exist in the form of orthorhombic or monoclinic crystals or as a liquid. Benzo[a]pyrene is produced during the incomplete combustion or pyrolysis of organic material and can be found in nature from volcanic eruptions and forest fires. It is also generated through human activities such as burning plants, wood, coal, and operating vehicles like cars and trucks. Additionally, it is present in some foods, pharmaceutical products, and tobacco smoke.

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  • 50-32-8 Structure
  • Basic information

    1. Product Name: BENZO[A]PYRENE
    2. Synonyms: 3,4-benz(a)pyrene;3,4-Benz[a]pyrene;3,4-Benzopirene;3,4-Benzpyren;3,4-BP;BP;coaltarpitchvolatiles:benzo(a)pyrene;Rcra waste number U022
    3. CAS NO:50-32-8
    4. Molecular Formula: C20H12
    5. Molecular Weight: 252.31
    6. EINECS: 200-028-5
    7. Product Categories: Industrial/Fine Chemicals;Benzo(a)pyrene and other PAH;Organics;Analytical Chemistry;Environmental Endocrine Disruptors;Estradiol, etc. (Environmental Endocrine Disruptors);Highly Purified Reagents;Other Categories;Refined Products by Sublimation;A-BAnalytical Standards;AromaticsAlphabetic;BA - BHChemical Class;Chemical Class;Hydrocarbons;NeatsAnalytical Standards;PAHsEnvironmental Standards;PAHsMore...Close...;A-BAlphabetic;Alpha Sort;B;BA - BHEnvironmental Standards;PAHs;Volatiles/ Semivolatiles;PAH
    8. Mol File: 50-32-8.mol
  • Chemical Properties

    1. Melting Point: 177-180°C
    2. Boiling Point: 495°C
    3. Flash Point: 495°C
    4. Appearance: Pale yellow/green/orange/Crystalline
    5. Density: 1.1549 (estimate)
    6. Vapor Pressure: 2.4 at 25 °C (McVeety and Hites, 1988)
    7. Refractive Index: 1.8530 (estimate)
    8. Storage Temp.: APPROX 4°C
    9. Solubility: Soluble in benzene, toluene, and xylene; sparingly soluble in ethanol and methanol (Windholz et al., 1983)
    10. PKA: >15 (Christensen et al., 1975)
    11. Water Solubility: Soluble in benzene, toluene, and xylene. Sparingly soluble in alcohol, methanol. Insoluble in water
    12. Stability: Stable. Incompatible with strong oxidizing agents.
    13. Merck: 14,1103
    14. BRN: 1911333
    15. CAS DataBase Reference: BENZO[A]PYRENE(CAS DataBase Reference)
    16. NIST Chemistry Reference: BENZO[A]PYRENE(50-32-8)
    17. EPA Substance Registry System: BENZO[A]PYRENE(50-32-8)
  • Safety Data

    1. Hazard Codes: T,N,F
    2. Statements: 45-46-50/53-60-61-43-67-66-36-11-65-38-52/53-36/37/38
    3. Safety Statements: 45-53-61-60-26-62-16
    4. RIDADR: 2811
    5. WGK Germany: 3
    6. RTECS: DJ3675000
    7. TSCA: Yes
    8. HazardClass: 6.1
    9. PackingGroup: III
    10. Hazardous Substances Data: 50-32-8(Hazardous Substances Data)

50-32-8 Usage

Uses

1. Used in Toxicological and Cancer Research:
Benzo[a]pyrene is extensively used in cancer research and for gas chromatography (GC) and liquid chromatography (LC) analysis. It serves as a multipurpose intermediate and a positive control in carcinogenicity studies due to its well-known carcinogenic properties.
2. Used in Rubber/Plastic Production:
Benzo[a]pyrene containing extender oil is utilized in the rubber and plastic industry to achieve the desired elasticity at a more affordable price.
3. Used in Paints and Coatings:
Benzo[a]pyrene containing coal tar pitch is employed in various paints or coatings as corrosion protection coats for hydraulic equipment, pipework, steel pilings in ports, vessels, and sealcoat products.
4. Used as Wood-Preservatives:
Benzo[a]pyrene can be used as a wood-preservative to prevent wood parasites and to protect wood from drying out.

References

https://monographs.iarc.fr/ENG/Monographs/vol100F/mono100F-14.pdf http://www.dhss.delaware.gov/dph/files/benzopyrenefaq.pdf https://greenliving.epa.gov.tw https://www.umweltbundesamt.de Barbara J. Mahler, Peter C. Van Metre, Judy L. Crane, Alison W. Watts, ?Mateo Scoggins, and E. Spencer Williams, Coal-Tar-Based Pavement Sealcoat and PAHs: Implications for the Environment, Human Health, and Stormwater Management, Environ Sci Technol, 2012, vol. 46, 3039-3045

Air & Water Reactions

Insoluble in water.

Reactivity Profile

BENZO[A]PYRENE undergoes photo-oxidation after irradiation in indoor sunlight or by fluorescent light in organic solvents. Incompatible with strong oxidizing agents including various electrophiles, peroxides, nitrogen oxides and sulfur oxides. Oxidized by ozone, chromic acid and chlorinating agents. Readily undergoes nitration and halogenation. Hydrogenation occurs with platinum oxide .

Hazard

Highly toxic, confirmed carcinogen by inhalation.

Health Hazard

The acute oral toxicity of benzo[a]pyrene islow. This may be due to the poor absorption of this compound by the gastrointestinal tract.The lethal dose in mice from intraperitonealadministration is reported as 500 mg/kg(NIOSH 1986).Animal studies show sufficient evidence ofits carcinogenicity by all routes of exposureaffecting a variety of tissues, which includethe lungs, skin, liver, kidney, and blood.Dasenbrock et al. (1996) have investigatedthe carcinogenic potency of carbon particles,diesel soot and benzo[a]pyrene in rats fromrepeated intracheal administration in a 16-week study. A total dose of 15 mg purebenzo[a]pyrene caused lung tumor in theexperimental animals at a rate similar tothat caused by diesel soot and carbon blackparticles.Lodovici et al. (1998) measured the levelsof PAHs and benzo[a]pyrenediol epoxideDNA adduct in autoptic lung samples ofsmokers and non-smokers. Benzo[a]pyrenediol epoxide resulting from metabolic activation of benzo[a]pyrene binds to DNA to forman adduct, the levels of which can be used as abiomarker to evaluate the exposure of humansto benzo(a)pyrene.Benz[a]pyrene exhibited teratogeniceffects in test species. It is a mutagen.It showed positive in a histidine rever-sion–Ames test, cell transform mouse embryotest, and in in vitro sister chromatid exchange(SCE)–human lymphocytes..

Fire Hazard

Literature sources indicate that BENZO[A]PYRENE is nonflammable.

Toxicology

benzo[a]pyrene (BP) is a reasonably potent contact carcinogen, and therefore has been subjected to extensive carcinogenic testing. A diet containing 25 ppm of benzo[a]pyrene (BP) fed to mice for 140 days produced leukemia and lung adenomas in addition to stomach tumors. Skin tumors developed in over 60% of the rats treated topically with approximately 10 mg of benzo[a]pyrene three times per week. The incidence of skin tumors dropped to about 20% when treatment was about 3 mg  3 per week. Above the 10 mg range, however, the incidence of skin tumors increased dramatically to nearly 100%. benzo[a]pyrene (BP) is also carcinogenic when administered orally. In one experiment, weekly doses of greater than 10 mg administered for 10 weeks induced stomach cancers, although no stomach cancers were produced at the dose of 10 mg or less. At 100 mg doses, nearly 79% of the animals had developed stomach tumors by the completion of the experiment. When 15 ppm of benzo[a]pyrene (BP) in feed was orally administered to mice, production of leukemia, lung adenomas, and stomach tumors were observed after 140 days.

Safety Profile

Confirmed carcinogen withexperimental carcinogenic, neoplastigenic, andtumorigenic data. A poison via subcutaneous,intraperitoneal, and intrarenal routes. Experimentalteratogenic and reproductive effects. Human mutation data reported. A skin irritant.

Potential Exposure

Benzopyrene (BP) is a PAH that has no commercial-scale production. B(a)P is produced in the United States by one chemical company and distributed by several specialty chemical companies in quantities from 100 mg to 5 g for research purposes. Although not manufactured in great quantity, B(a)P is a by-product of combustion. It is estimated that 1.8 million pounds per year are released from stationary sources, with 96% coming from: (1) coal refuse piles, outcrops, and abandoned coal mines; (2) residential external combustion of bituminous coal; (3) coke manufacture; and (4) residential external combustion of anthracite coal. Human exposure to B(a)P can occur from its presence as a by-product of chemical production. The number of persons exposed is not known. Persons working at airports in tarring operations; refuse incinerator operations; power plants, and coke manufacturers, may be exposed to higher B(a)P levels than the general population. Scientists involved in cancer research or in sampling toxic materials may also be occupationally exposed. The general population may be exposed to B(a)P from air pollution, cigarette smoke, and food sources. B(a) P has been detected in cigarette smoke at levels ranging from 0.2 to 12.2:g per 100 cigarettes. B(a)P has been detected at low levels in foods ranging from 0.1 to 50 ppb.

Source

MCLG: zero; MCL: 0.2 μg/L (U.S. EPA, 2000). Identified in Kuwait and South Louisiana crude oils at concentrations of 2.8 and 0.75 ppm, respectively (Pancirov and Brown, 1975). Emitted to the environment from coke production, coal refuse and forest fires, motor vehicle exhaust, and heat and power (utility) generation (Suess, 1976). Benzo[a]pyrene is produced from combustion of tobacco and fuels. It is also a component of gasoline (133–143 μg/L), fresh motor oil (20 to 100 g/kg), used motor oil (83.2 to 242.4 mg/kg), asphalt (≤0.0027 wt %), coal tar pitch (≤1.25 wt %), cigarette smoke (25 μg/1,000 cigarettes), and gasoline exhaust (quoted, Verschueren, 1983). Detected in asphalt fumes at an average concentration of 14.72 ng/m3 (Wang et al., 2001). Benzo[a]pyrene was also detected in liquid paraffin at an average concentration of 25 μg/kg (Nakagawa et al., 1978). Benzo[a]pyrene was reported in a variety of foodstuffs including raw and cooked meat (ND to 12 ppb), fish (0.3–6.9 ppb), vegetables oils (ND-4), fruits (ND to 6.2 ppb) (quoted, Verschueren, 1983). The concentration of benzo[a]pyrene in coal tar and the maximum concentration reported in groundwater at a mid-Atlantic coal tar site were 3,600 and 0.0058 mg/L, respectively (Mackay and Gschwend, 2001). Based on laboratory analysis of 7 coal tar samples, benzo[a]pyrene concentrations ranged from 500 to 6,400 ppm (EPRI, 1990). In three high-temperature coal tars, benzo[a]pyrene concentrations ranged from 5,300 to 7,600 mg/kg (Lehmann et al., 1984). Benzo[a]pyrene was identified in a U.S. commercial creosote at an approximate concentration of 0.3% (Black, 1982). Nine commercially available creosote samples contained benzo[a]pyrene at concentrations ranging from 2 to 160 mg/kg (Kohler et al., 2000). Identified in high-temperature coal tar pitches used in roofing operations at concentrations ranging from 4,290 to 13,200 mg/kg (Arrendale and Rogers, 1981; Malaiyandi et al., 1982). Lee et al. (1992a) equilibrated 8 coal tars with distilled water at 25 °C. The maximum concentration of benzo[a]pyrene observed in the aqueous phase was 1 μg/L. 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[a]pyrene were 0.712 mg/kg of pine burned, 0.245 mg/kg of oak burned, and 0.301 mg/kg of eucalyptus burned.Particle-phase tailpipe emission rates from gasoline-powered automobiles with and without catalytic converters were 0.021 and 41.0 μg/km, respectively (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[a]pyrene emitted ranged from 39.4 ng/kg at 650 °C to 690.7 ng/kg at 850 °C. The greatest amount of PAHs emitted were observed at 750 °C (Mastral et al., 1999).

Environmental fate

The main natural sources of Benzo[a]pyrene(BaP) are forest fires and erupting volcanoes. Anthropogenic sources include the combustion of fossil fuels, coke oven emis- sions, and vehicle exhausts. In surface waters, direct deposition from the atmosphere appears to be the major source of BaP. Benzo[a]pyrene is moderately persistent in the environment. It readily binds to soils and does not readily leach to groundwater, though it has been detected in some groundwater. If released to water, it sorbs very strongly to sediments and particulate matter. In most waters and sediments, it resists breakdown by microbes or reactive chemicals, but it may evaporate or be degraded by sunlight. In water supply systems, it tends to sorb to any particulate matter and be removed by filtration before reaching the tap. In tap water, its source is mainly from PAH-containing materials in water storage and distribution systems.

Purification Methods

A solution of 250mg of benzo[a]pyrene in 100mL of *benzene is diluted with an equal volume of hexane, then passed through a column of alumina, Ca(OH)2 and Celite (3:1:1). The adsorbed material is developed with a 2:3 *benzene/hexane mixture. (It showed as an intensely fluorescent zone.) The main zone is eluted with 3:1 acetone/EtOH, and is transferred into 1:1 *benzene-hexane by adding H2O. The solution is washed, dried with Na2SO4, evaporated and crystallised from *benzene by the addition of MeOH [Lijinsky & Zechmeister J Am Chem Soc 75 5495 1953]. Alternatively it can be chromatographed on activated alumina, eluted with a cyclohexane-*benzene mixture containing up to 8% *benzene, and the solvent evaporated under reduced pressure [Cahnmann Anal Chem 27 1235 1955], and crystallised from EtOH [Nithipatikom & McGown Anal Chem 58 3145 1986]. [Beilstein 5 III 2517, 5 IV 2687.] CARCINOGENIC.

Toxicity evaluation

BaP is purposely synthesized solely for laboratory studies. The primary source of BaP and many PAHs in air is the incomplete combustion of wood, gasoline, and other fuels; in industrial settings where coal is burned; and in natural burns such as forest fires. BaP can bind to particulate matter, and inhalation is a common route of exposure. BaP is poorly water soluble, partitioning strongly to the sediment, and does not readily bioaccumulate. BaP is found in fossil fuels, crude oils, shale oils, and coal tars, and is emitted with gases and fly ash from active volcanoes. If released to air, an extrapolated vapor pressure of 5.49×10-9 mm Hg at 25°C indicates BaP will exist solely in the particulate phase in the atmosphere. Particulate-phase BaP is usually removed from the atmosphere by wet or dry deposition. BaP contains chromophores that absorb at wavelengths >290 nm and therefore is expected to be susceptible to direct photolysis by sunlight; after 17 h irradiation with light >290 nm, 26.5% of BaP adsorbed onto silica gel was degraded. If released to soil, BaP is expected to have very low to no mobility based on measured soil Koc values of 930–6300. Volatilization from moist soil surfaces is not expected to be an important fate process based on a Henry’s Law constant of 4.57×10-7 atm m3 mol1. The stability of BaP in soil is expected to vary depending on the nature of compounds accompanying it and the nature and previous history of the soil; biodegradation half-lives of 309 and 229 days were observed in Kidman and McLaurin sandy loam soils, respectively. BaP is expected to adsorb to suspended solids and sediment based on the measured Koc values, when released into water. Biodegradation of BaP is possible in aquatic systems. Volatilization from water surfaces is not expected to be an important fate process based on this compound’s Henry’s Law constant. Measured bioconcentration values ranging from 8.7 to 1×10105 suggest bioconcentration in aquatic organisms can be low to very high. Hydrolysis is not expected to be an important environmental fate process since this compound lacks functional groups that hydrolyze under environmental conditions.

Incompatibilities

Incompatible with oxidizers (chlorates, nitrates, peroxides, permanganates, perchlorates, chlorine, bromine, fluorine, etc.); contact may cause fires or explosions. Keep away from alkaline materials, strong bases, strong acids, oxoacids, epoxides, nitrogen dioxide and ozone.

Waste Disposal

Incineration in admixture with a flammable solvent.

Check Digit Verification of cas no

The CAS Registry Mumber 50-32-8 includes 5 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 2 digits, 5 and 0 respectively; the second part has 2 digits, 3 and 2 respectively.
Calculate Digit Verification of CAS Registry Number 50-32:
(4*5)+(3*0)+(2*3)+(1*2)=28
28 % 10 = 8
So 50-32-8 is a valid CAS Registry Number.
InChI:InChI=1/C20H12/c1-2-7-17-15(4-1)12-16-9-8-13-5-3-6-14-10-11-18(17)20(16)19(13)14/h1-12H

50-32-8 Well-known Company Product Price

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  • Alfa Aesar

  • (15856)  Benzo[a]pyrene, 96%   

  • 50-32-8

  • 100mg

  • 879.0CNY

  • Detail
  • Alfa Aesar

  • (15856)  Benzo[a]pyrene, 96%   

  • 50-32-8

  • 0.5g

  • 3514.0CNY

  • Detail
  • Sigma-Aldrich

  • (51968)  Benzo[a]pyrene  certified reference material, TraceCERT®

  • 50-32-8

  • 51968-50MG

  • 1,075.23CNY

  • Detail
  • Supelco

  • (CRM40071)  Benzo[a]pyrenesolution  certified reference material, TraceCERT®, 1000 μg/mL in acetone

  • 50-32-8

  • CRM40071

  • 342.81CNY

  • Detail
  • Supelco

  • (CRM48665)  Benzo[a]pyrenesolution  certified reference material, TraceCERT®, 200 μg/mL in methylene chloride

  • 50-32-8

  • CRM48665

  • 273.78CNY

  • Detail
  • Sigma-Aldrich

  • (31306)  Benzo[a]pyrenesolution  100 μg/mL in cyclohexane, analytical standard

  • 50-32-8

  • 31306-2ML

  • 610.74CNY

  • Detail
  • Sigma-Aldrich

  • (31306)  Benzo[a]pyrenesolution  100 μg/mL in cyclohexane, analytical standard

  • 50-32-8

  • 31306-10ML

  • 1,189.89CNY

  • Detail
  • Supelco

  • (48564)  Benzo[a]pyrene  analytical standard, for environmental analysis

  • 50-32-8

  • 000000000000048564

  • 2,163.33CNY

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50-32-8SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 11, 2017

Revision Date: Aug 11, 2017

1.Identification

1.1 GHS Product identifier

Product name benzo[a]pyrene

1.2 Other means of identification

Product number -
Other names benzo(a)pyrene

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only. Food Contaminant: CONTAMINANT
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
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More Details:50-32-8 SDS

50-32-8Synthetic route

2-[2,6-di(2-methoxyethenyl)phenyl]naphthalene

2-[2,6-di(2-methoxyethenyl)phenyl]naphthalene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With bismuth(lll) trifluoromethanesulfonate In 1,2-dichloro-ethane at 25℃; for 2h; Inert atmosphere; Schlenk technique;90%
With methanesulfonic acid In dichloromethane at 0℃;57%
5-ethynylchrysene
1393794-15-4

5-ethynylchrysene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With platinum(II) chloride In toluene at 80℃;65%
9,10-dihydro benzopyrene
17573-15-8

9,10-dihydro benzopyrene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
palladium on activated charcoal at 300 - 305℃;60%
With KO2; 18-crown-6 ether In N,N-dimethyl-formamide for 20h; Ambient temperature;86 % Chromat.
cis-4,5-Diacetoxy-4,5-dihydrobenzopyrene
56182-92-4

cis-4,5-Diacetoxy-4,5-dihydrobenzopyrene

A

benzopyrene
50-32-8

benzopyrene

B

4-Acetoxybenzopyrene
56182-98-0

4-Acetoxybenzopyrene

C

5-Acetoxybenzopyrene
24027-82-5

5-Acetoxybenzopyrene

Conditions
ConditionsYield
With toluene-4-sulfonic acid In benzene for 4h; Heating;A n/a
B 30%
C 11%
1,8-bis(ethynyl)naphthalene
18067-44-2

1,8-bis(ethynyl)naphthalene

2-(trimethylsilyl)phenyl trifluoromethanesulfonate
88284-48-4

2-(trimethylsilyl)phenyl trifluoromethanesulfonate

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With fluoride In tetrahydrofuran Ambient temperature;30%
Benzopyrene radical cation perchlorate

Benzopyrene radical cation perchlorate

A

benzopyrene
50-32-8

benzopyrene

B

6-fluorobenzopyrene
59417-86-6

6-fluorobenzopyrene

Conditions
ConditionsYield
With Tetramethylammonium dihydrogen trifluoride In acetonitrile for 1h;A n/a
B 25%
benzenedizolium-2-carboxylate
1608-42-0

benzenedizolium-2-carboxylate

1,8-bis(ethynyl)naphthalene
18067-44-2

1,8-bis(ethynyl)naphthalene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
In 1,2-dichloro-ethane Heating;23%
Benzopyrene radical cation tetrafluoroborate

Benzopyrene radical cation tetrafluoroborate

A

benzopyrene
50-32-8

benzopyrene

B

6-fluorobenzopyrene
59417-86-6

6-fluorobenzopyrene

Conditions
ConditionsYield
With Tetramethylammonium dihydrogen trifluoride In acetonitrile for 1h;A n/a
B 20%
4,5-dihydro(epoxy) benzopyrene
37574-47-3, 72010-12-9, 72010-13-0

4,5-dihydro(epoxy) benzopyrene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With tetraphenylporphinatoiron(II)(pyridine)2 for 60h; Ambient temperature;8%
1,6,10b,11,12,12a-hexahydro-2H-benzo[def]chrysen-3-one
61441-28-9

1,6,10b,11,12,12a-hexahydro-2H-benzo[def]chrysen-3-one

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With potassium hydroxide; hydrazine hydrate; diethylene glycol Erhitzen des Reaktionsprodukts an Palladium auf 300-320grad;
7-hydroxy-7,8,9,10-tetrahydrobenzopyrene
6272-55-5

7-hydroxy-7,8,9,10-tetrahydrobenzopyrene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With palladium on activated charcoal at 310 - 320℃;
Multi-step reaction with 2 steps
1: 93 percent / glacial acetic acid, conc. HCl / 0.25 h
2: 60 percent / 10percent palladium on charcoal / 300 - 305 °C
View Scheme
2'-ethyl-3,4,5,6,7,8-hexahydro-1H-spiro[anthracene-2,1'-cyclopentane]
875235-70-4

2'-ethyl-3,4,5,6,7,8-hexahydro-1H-spiro[anthracene-2,1'-cyclopentane]

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With platinum on activated charcoal at 350℃;
5-hydroxy-3-oxo-2,3,11,12-tetrahydro-1H-benzo[def]chrysene-12a-carboxylic acid methyl ester
109729-99-9

5-hydroxy-3-oxo-2,3,11,12-tetrahydro-1H-benzo[def]chrysene-12a-carboxylic acid methyl ester

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With zinc
7,8,9,10-tetrahydrobenzo[a]pyrene
17750-93-5

7,8,9,10-tetrahydrobenzo[a]pyrene

A

benzopyrene
50-32-8

benzopyrene

B

7,8-dihydrobenzopyrene
17573-23-8

7,8-dihydrobenzopyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone In benzene for 5h; Ambient temperature; Title compound not separated from byproducts;A 19 % Chromat.
B 66 % Chromat.
11,12-dihydrobenzopyrene
81194-83-4

11,12-dihydrobenzopyrene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone In benzene for 2h; Heating; Yield given;
pyrene
129-00-0

pyrene

1,4-dichlorobutane
110-56-5

1,4-dichlorobutane

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With 2,3-dicyano-5,6-dichloro-p-benzoquinone; aluminium trichloride 1.) carbon disulfide, reflux, 1 h; 2.) toluene, reflux; Yield given. Multistep reaction;
Benzopyrene radical cation perchlorate

Benzopyrene radical cation perchlorate

A

benzo[a]pyrene-6,12-dione
3067-12-7

benzo[a]pyrene-6,12-dione

B

benzopyrene
50-32-8

benzopyrene

C

benzo[a]pyrene-1,6-quinone
3067-13-8

benzo[a]pyrene-1,6-quinone

D

benzo[a]pyrene-3,6-dione
3067-14-9

benzo[a]pyrene-3,6-dione

Conditions
ConditionsYield
With water for 0.25h; Yield given. Yields of byproduct given. Title compound not separated from byproducts;
9,10-dihydro benzopyrene
17573-15-8

9,10-dihydro benzopyrene

A

benzopyrene
50-32-8

benzopyrene

B

(7R,8S)-7,8-epoxy-7,8,9,10-tetrahydrobenzopyrene
68906-75-2

(7R,8S)-7,8-epoxy-7,8,9,10-tetrahydrobenzopyrene

C

(7S,8R)-7,8-epoxy-7,8,9,10-tetrahydrobenzopyrene
68906-81-0

(7S,8R)-7,8-epoxy-7,8,9,10-tetrahydrobenzopyrene

Conditions
ConditionsYield
With sodium hypochlorite; tetralin; Jacobsen's catalyst In dichloromethane at 0℃; for 2.5h; Yield given. Yields of byproduct given. Title compound not separated from byproducts;
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;
2-monochlorophenol
95-57-8

2-monochlorophenol

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
In various solvent(s) at 399.85℃; Condensation; Formation of xenobiotics;
U.S. low sulfur petroleum diesel fuel

U.S. low sulfur petroleum diesel fuel

benzopyrene
50-32-8

benzopyrene

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

100 percent soy methyl ester biodiesel fuel

benzopyrene
50-32-8

benzopyrene

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

methyl chloride; methane; mixture of

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With air Oxidation; Formation of xenobiotics;
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 tire

waste tire

A

pyrene
129-00-0

pyrene

B

9H-fluorene
86-73-7

9H-fluorene

C

chrysene
218-01-9

chrysene

D

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With air at 850 - 950℃; Oxidation; Formation of xenobiotics;
pulp and paper-generated biowaste

pulp and paper-generated biowaste

A

9H-fluorene
86-73-7

9H-fluorene

B

phenanthrene
85-01-8

phenanthrene

C

benzopyrene
50-32-8

benzopyrene

D

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

cyclopenta[c,d]pyrene

Conditions
ConditionsYield
With air at 1496.85℃; Oxidation; Formation of xenobiotics;
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;
aluminium trichloride
7446-70-0

aluminium trichloride

tetralin
119-64-2

tetralin

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
at 70℃;
4,5,5a,6,6a,7,8,9,10.10a-decahydro-(5ar,6aξ,10ac)-benzo-chrysene

4,5,5a,6,6a,7,8,9,10.10a-decahydro-(5ar,6aξ,10ac)-benzo-chrysene

benzopyrene
50-32-8

benzopyrene

Conditions
ConditionsYield
With palladium on activated charcoal at 300 - 320℃;
benzopyrene
50-32-8

benzopyrene

4,5-dihydrobenzopyrene
57652-66-1

4,5-dihydrobenzopyrene

Conditions
ConditionsYield
With hydrogen; palladium on activated charcoal In ethyl acetate under 1034.3 Torr; for 24h; Product distribution; Ambient temperature;100%
With hydrogen; palladium on activated charcoal In ethyl acetate under 1034.3 Torr; for 24h; Ambient temperature;100%
With hydrogen; Pd/SrCO3
benzopyrene
50-32-8

benzopyrene

6-Chlorobenzo[a]pyrene
21248-01-1

6-Chlorobenzo[a]pyrene

Conditions
ConditionsYield
With copper dichloride In tetrachloromethane for 16h; Heating;95%
With sulfuryl dichloride In 1,2-dichloro-ethane at 20℃; for 1h; Chlorination;88%
With copper dichloride In tetrachloromethane Heating;68%
benzopyrene
50-32-8

benzopyrene

Mangantriacetat

Mangantriacetat

A

benzo[a]pyrene-6,12-dione
3067-12-7

benzo[a]pyrene-6,12-dione

B

benzopyren-6-yl acetate
53555-67-2

benzopyren-6-yl acetate

C

benzo[a]pyrene-1,6-quinone
3067-13-8

benzo[a]pyrene-1,6-quinone

D

benzo[a]pyrene-3,6-dione
3067-14-9

benzo[a]pyrene-3,6-dione

Conditions
ConditionsYield
In acetic acid at 40℃; for 0.166667h; Product distribution; Mechanism; other 6-, 1,6-, and 3,6-substituted benzo<a>pyrenes</a>;A n/a
B 90%
C n/a
D n/a
In acetic acid at 40℃; for 0.5h;A n/a
B 90%
C n/a
D n/a
benzopyrene
50-32-8

benzopyrene

A

benzo[a]pyrene-6,12-dione
3067-12-7

benzo[a]pyrene-6,12-dione

B

benzopyren-6-yl acetate
53555-67-2

benzopyren-6-yl acetate

C

benzo[a]pyrene-1,6-quinone
3067-13-8

benzo[a]pyrene-1,6-quinone

D

benzo[a]pyrene-3,6-dione
3067-14-9

benzo[a]pyrene-3,6-dione

Conditions
ConditionsYield
With manganese triacetate In acetic acid at 40℃; for 0.5h; Title compound not separated from byproducts;A n/a
B 90%
C n/a
D n/a
benzopyrene
50-32-8

benzopyrene

7,8,9,10-tetrahydrobenzo[a]pyrene
17750-93-5

7,8,9,10-tetrahydrobenzo[a]pyrene

Conditions
ConditionsYield
With hydrogen; platinum(IV) oxide; platinum on activated charcoal In ethyl acetate Product distribution; Ambient temperature;86%
With hydrogen; platinum(IV) oxide; platinum on activated charcoal In ethyl acetate Ambient temperature;86%
With cyclohexane; acetic acid; platinum Hydrogenation;
benzopyrene
50-32-8

benzopyrene

6-Bromobenzo[a]pyrene
21248-00-0

6-Bromobenzo[a]pyrene

Conditions
ConditionsYield
With N-Bromosuccinimide In tetrachloromethane for 3h; Heating;86%
With bromine In carbon disulfide Ambient temperature;85%
With pyridinium hydrobromide perbromide In acetic acid for 1h;80%
[(η5-Me5C5)Co]2-μ-(η4:η4-toluene)

[(η5-Me5C5)Co]2-μ-(η4:η4-toluene)

benzopyrene
50-32-8

benzopyrene

[(η5-pentamethylcyclopentadienyl)cobalt(η4:7,11-benzo[a]pyrene)]
656821-05-5

[(η5-pentamethylcyclopentadienyl)cobalt(η4:7,11-benzo[a]pyrene)]

Conditions
ConditionsYield
In benzene under inert gas; soln. of Co-complex and benzo(a)pyrene in benzene stirred for 24 h; volatiles removed under vac., residue dissolved in Et2O, filtered, filtrate concd., cooled to -30°C; elem. anal.;82%
benzopyrene
50-32-8

benzopyrene

6-iodobenzopyrene
39000-82-3

6-iodobenzopyrene

Conditions
ConditionsYield
With aluminum oxide; N-iodo-succinimide In toluene at 20℃; for 96h;80%
With aluminum oxide; iodine; benzene
With aluminum oxide; N-iodo-succinimide In toluene at 20℃; for 48h;455.2 mg
benzopyrene
50-32-8

benzopyrene

C20H12(1+)*BF4(1-)

C20H12(1+)*BF4(1-)

Conditions
ConditionsYield
With nitrosonium tetrafluoroborate In acetonitrile Radical cation formation;78%
benzopyrene
50-32-8

benzopyrene

2,7-Dihydroxynaphthalene
582-17-2

2,7-Dihydroxynaphthalene

C30H18O2

C30H18O2

Conditions
ConditionsYield
With iron(III) chloride; di-tert-butyl peroxide at 20 - 40℃; for 4h;77%
benzopyrene
50-32-8

benzopyrene

tert-butyl alcohol
75-65-0

tert-butyl alcohol

A

9-tert-butylbenzopyrene
80484-55-5

9-tert-butylbenzopyrene

B

2,9-di-tert-butylbenzopyrene
80484-71-5

2,9-di-tert-butylbenzopyrene

Conditions
ConditionsYield
In trifluoroacetic acid for 23h; Heating;A 64%
B n/a
In trifluoroacetic acid for 23h; Heating;A 64%
B 50 mg
benzopyrene
50-32-8

benzopyrene

N-methyl-N-phenylformamide
93-61-8

N-methyl-N-phenylformamide

benzpyrene-6-carbaldehyde
13312-42-0

benzpyrene-6-carbaldehyde

Conditions
ConditionsYield
With 1,2-dichloro-benzene; trichlorophosphate at 95 - 100℃; for 2h;54%
With trichlorophosphate
With trichlorophosphate
benzopyrene
50-32-8

benzopyrene

A

3-(benzo[a]pyren-6-yl)adenine

3-(benzo[a]pyren-6-yl)adenine

B

1-(benzo[a]pyren-6-yl)adenine

1-(benzo[a]pyren-6-yl)adenine

C

7-(benzo[a]pyren-6-yl)adenine

7-(benzo[a]pyren-6-yl)adenine

Conditions
ConditionsYield
With potassium perchlorate In N,N-dimethyl-formamide Addition; Electrochemical reaction;A 5.6%
B 52%
C 1.7%
benzopyrene
50-32-8

benzopyrene

A

6-nitrobenzo(a)pyrene
63041-90-7

6-nitrobenzo(a)pyrene

B

3-nitrobenzopyrene
70021-98-6

3-nitrobenzopyrene

C

1-nitrobenzopyrene
70021-99-7

1-nitrobenzopyrene

D

3,6-dinitrobenzopyrene
128714-76-1

3,6-dinitrobenzopyrene

E

1,6-dinitrobenzopyrene
128714-75-0

1,6-dinitrobenzopyrene

Conditions
ConditionsYield
With nitric acid In acetic anhydride for 0.5h; Product distribution; Ambient temperature; other reaction time;A n/a
B n/a
C n/a
D 13%
E 28%
benzopyrene
50-32-8

benzopyrene

6-fluorobenzopyrene
59417-86-6

6-fluorobenzopyrene

Conditions
ConditionsYield
With N-fluoro-2,4-dinitroimidazole In 1,2-dichloro-ethane for 72h; Heating;22%
Multi-step reaction with 2 steps
1: 80 percent / PyHBr3 / acetic acid / 1 h
2: 1.) n-C4H9Li, 2.) perchloryl fluoride / 1.) THF, hexane, -55 deg C, 45 min
View Scheme
benzopyrene
50-32-8

benzopyrene

sodium acetate
127-09-3

sodium acetate

A

benzo[a]pyrene-6,12-dione
3067-12-7

benzo[a]pyrene-6,12-dione

B

benzopyren-6-yl acetate
53555-67-2

benzopyren-6-yl acetate

C

benzo[a]pyrene-1,6-quinone
3067-13-8

benzo[a]pyrene-1,6-quinone

D

benzo[a]pyrene-3,6-dione
3067-14-9

benzo[a]pyrene-3,6-dione

Conditions
ConditionsYield
Stage #1: benzo<a>pyrene</a> With iodine; silver perchlorate In benzene Radical cation*AgI formation;
Stage #2: sodium acetate In water; acetonitrile Substitution;
A n/a
B 11%
C n/a
D n/a
benzopyrene
50-32-8

benzopyrene

4,5-dihydro(epoxy) benzopyrene
37574-47-3, 72010-12-9, 72010-13-0

4,5-dihydro(epoxy) benzopyrene

Conditions
ConditionsYield
With 18-crown-6 ether; (COCl2)2 In hexane at -10 - -5℃;5%
benzopyrene
50-32-8

benzopyrene

(bromomethyl)pentafluorobenzene
1765-40-8

(bromomethyl)pentafluorobenzene

2,3-bis(pentafluorobenzyl)pyrenedicarboxylate

2,3-bis(pentafluorobenzyl)pyrenedicarboxylate

Conditions
ConditionsYield
Stage #1: benzo<a>pyrene</a> With 18-crown-6 ether In N,N-dimethyl-formamide at 20℃; for 20h; Oxidation;
Stage #2: (bromomethyl)pentafluorobenzene With triethylamine In toluene at 50℃; for 6h; Esterification; capped tube;
0.14%
tetrachloromethane
56-23-5

tetrachloromethane

thiocyanogen
505-14-6

thiocyanogen

benzopyrene
50-32-8

benzopyrene

benzo[def]chrysen-6-ylsulfanyl cyanate
54064-38-9

benzo[def]chrysen-6-ylsulfanyl cyanate

2,2'-azobis(isobutyronitrile)
78-67-1

2,2'-azobis(isobutyronitrile)

benzopyrene
50-32-8

benzopyrene

2,2'-dimethyl-2,2'-(11,12-dihydro-benzo[def]chrysene-11,12-diyl)-di-propionitrile

2,2'-dimethyl-2,2'-(11,12-dihydro-benzo[def]chrysene-11,12-diyl)-di-propionitrile

thiocyanogen
505-14-6

thiocyanogen

benzopyrene
50-32-8

benzopyrene

benzo[def]chrysen-6-ylsulfanyl cyanate
54064-38-9

benzo[def]chrysen-6-ylsulfanyl cyanate

Conditions
ConditionsYield
With tetrachloromethane

50-32-8Relevant articles and documents

Regioselective arene homologation through rhenium-catalyzed deoxygenative aromatization of 7-oxabicyclo[2.2.1]hepta-2,5-dienes

Murai, Masahito,Ogita, Takuya,Takai, Kazuhiko

, p. 2332 - 2335 (2019/02/27)

Combined use of oxorhenium catalysts with triphenyl phosphite as an oxygen acceptor allowed efficient deoxygenative aromatization of oxabicyclic dienes. The reaction proceeded under neutral conditions and was compatible with various functional groups. Combining this deoxygenation with regioselective bromination and trapping of the generated aryne with furan resulted in benzannulative π-extension at the periphery of the PAHs. This enabled direct use of unfunctionalized PAHs for extension of π-conjugation. Iteration of the transformations increased the number of fused-benzene rings one at a time, which has the potential to alter the properties of PAHs by fine-tuning the degree of π-conjugation, shape, and edge topology.

Bismuth-catalyzed synthesis of polycyclic aromatic hydrocarbons (PAHs) with a phenanthrene backbone via cyclization and aromatization of 2-(2-arylphenyl)vinyl ethers

Murai, Masahito,Hosokawa, Naoki,Roy, David,Takai, Kazuhiko

supporting information, p. 4134 - 4137 (2014/09/30)

The reaction of 2-(2-arylphenyl)vinyl ethers in the presence of a catalytic amount of bismuth(III) triflate gave substituted phenanthrenes in excellent yields under mild reaction conditions. The reaction was also applied to the construction of other polycyclic aromatic hydrocarbons (PAHs), such as chrysene, helicene, and pyrene having a phenanthrene backbone, via regioselective cyclization. This method has the advantages of easy availability of the cyclization precursors, operational simplicity, and high reaction efficiency.

Synthesis of 13C4-labelled oxidized metabolites of the carcinogenic polycyclic aromatic hydrocarbon benzo[a]pyrene

Wu, Anhui,Xu, Daiwang,Lu, Ding,Penning, Trevor M.,Blair, Ian A.,Harvey, Ronald G.

, p. 7217 - 7233 (2012/09/05)

Polycyclic aromatic hydrocarbons (PAHs), such as benzo[a]pyrene (BaP), are ubiquitous environmental contaminants that are implicated in causing lung cancer. BaP is a component of tobacco smoke that is transformed enzymatically to active forms that interact with DNA. We reported previously development of a sensitive stable isotope dilution LC/MS method for analysis of BaP metabolites. We now report efficient syntheses of 13C4-BaP and the complete set of its 13C4-labelled oxidized metabolites needed as internal standards They include the metabolites not involved in carcinogenesis (Group A) and the metabolites implicated in initiation of cancer (Group B). The synthetic approach is novel, entailing use of Pd-catalyzed Suzuki, Sonogashira, and Hartwig cross-coupling reactions combined with PtCl2-catalyzed cyclization of acetylenic compounds. This synthetic method requires fewer steps, employs milder conditions, and product isolation is simpler than conventional methods of PAH synthesis. The syntheses of 13C4-BaP and 13C4-BaP-8-ol each require only four steps, and the 13C-atoms are all introduced in a single step. 13C4-BaP-8-ol serves as the synthetic precursor of all the oxidized metabolites of 13C-BaP implicated in initiation of cancer. The isotopic purities of the synthetic 13C 4-BaP metabolites were estimated to be ≥99.9%.

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.

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.

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.

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.

Emissions of air pollutants from household stoves: Honeycomb coal versus coal cake

Ge, Su,Xu, Xu,Chow, Judith C.,Watson, John,Sheng, Qing,Liu, Weili,Bai, Zhipeng,Zhu, Tan,Zhang, Junfeng

, p. 4612 - 4618 (2007/10/03)

Domestic coal combustion can emit various air pollutants. In the present study, we measured emissions of particulate matter (PM) and gaseous pollutants from burning a specially formulated honeycomb coal (H-coal) and a coal cake (C-coal). Flue gas samples for PM2.5, PM coarse (PM 2.5-10), and TSP were collected isokinetically using a cascade impactor; PM mass concentrations were determined gravimetrically. Concentrations of SO2, NOx, and ionic Cr(VI) in PM were analyzed using spectrometric methods. Fluoride concentrations were measured using a specific ion electrode method. PM elemental components were analyzed using an X-ray fluorescence technique. Total (gas and particle phase) benzo[a]pyrene (BaP) concentration was determined using an HPLC/fluorescence method. Elemental and organic carbon contents of PM were analyzed using a thermal/optical reflectance technique. The compositional and structural differences between the H-coal and C-coal resulted in different emission characteristics. In generating 1 MJ of delivered energy, the H-coal resulted in a significant reduction in emissions of SO2 (by 68%), NOx (by 47%), and TSP (by 56%) as compared to the C-coal, whereas the emissions of PM2.5 and total BaP from the H-coal combustion were 2-3-fold higher, indicating that improvements are needed to further reduce emissions of these pollutants in developing future honeycomb coals. Although the H-coal and the C-coal had similar emission factors for gas-phase fluoride, the H-coal had a particle-phase fluoride emission factor that was only half that of the C-coal. The H-coal had lower energy-based emissions of all the measured toxic elements in TSP but higher emissions of Cd and Ni in PM2.5.

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