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106-51-4 Usage

Description

Quinone (p-benzoquinone) exists as a large yellow, monoclinic prism with an irritating odour resembling that of chlorine. Quinone is extensively used as a chemical intermediate, a polymerisation inhibitor, an oxidising agent, a photographic chemical, a tanning agent, and a chemical reagent. Quinone (p-benzoquinone) was first produced commercially in 1919 and has since been manufactured in several European countries. Its major use is in hydroquinone production, but it is also used as a polymerisation inhibitor and as an intermediate in the production of a variety of substances, including rubber accelerators and oxidising agents. It is used in the dye, textile, chemical, tanning, and cosmetic industries. In chemical synthesis for hydroquinone and other chemicals, quinone is used as an intermediate. It is also used in the manufacturing industries and chemical laboratory associated with protein fibre, photographic film, hydrogen peroxide, and gelatin making. Occupational exposure to quinone may occur in the dye, textile, chemical, tanning, and cosmetic industries. Inhalation exposure to quinone may occur from tobacco smoke.

Chemical Properties

Quinone is a yellow, crystalline material or large yellow, monoclinic prisms. Pungent, irritating odor. 1,4-Benzoquinone or p-benzoquinone is the basic structure of quinonoid compounds.They are widely distributed in the natural world, being found in bacteria, plants and arthropods and hence quinones are ubiquitous to living systems. Quinones play pivotal role in biological functions including oxidative phosphorylation and electron transfer.

Physical properties

Light yellow crystals with an acrid odor resembling chlorine. Odor threshold concentration is 84 ppb (quoted, Amoore and Hautala, 1983).

Uses

1,4-Benzoquinone is used in the manufacture of dyes, fungicide, and hydroquinone; for tanning hides; as an oxidizing agent; in photography; making gelatin insoluble; strengthening animal fibers and as reagent.

Preparation

Preparation of Quinone (p-Benzoquinone) from Hydroquinone. Principle: Hydroquinone can be readily oxidized to quinone by using oxidizing agent like potassium dichromate and conc. H2SO4 or KBrO3. Reaction: Procedure: Take 0.5 g hydroquinone and 5 ml distilled water in a beaker (25 ml). Heat on a wire gauze to obtain a clear solution. Take 1 g potassium dichromate (K2Cr2O7) in a conical flask and dissolve in 10 ml water and add 1 ml conc. H2SO4. Shake and cool the conical flask in ice water. To this ice cold solution add hydroquinone solution (prepared above) dropwise over a period of 30 minutes with constant shaking. Do not allow the temperature to rise above 20oC. After complete addition, continue shaking for further 10 minutes. Yellow crystals of quinone separate out. Filter on a Buchner funnel and dry it well. (Note: Do not wash with water as the product is water soluble). Record the practical yield and re-crystallize from ethyl alcohol. Re-crystallization: Dissolve the crude product in minimum amount of ethyl alcohol in a beaker by heating on a water bath. Filter the hot solution and cool the filtrate. The yellow needles of quinone separate out. Filter, dry and record the melting point and TLC (using toluene as a solvent).

Definition

ChEBI: 1,4-benzoquinone is the simplest member of the class of 1,4-benzoquinones, obtained by the formal oxidation of hydroquinone to the corresponding diketone. It is a metabolite of benzene. It has a role as a cofactor, a human xenobiotic metabolite and a mouse metabolite.

Production Methods

Quinone was produced as early as 1838 by oxidation of quinic acid with manganese dioxide. Quinone can be prepared by oxidation starting with aniline or by the oxidation of hydroquinone with bromic acid. More recently, quinone has been made biosynthetically from D-glucose.

Application

p-Benzoquinone is used as a dienophile in Diels-Alder cycloadditions to prepare naphthoquinones and 1,4-phenanthrenediones. It acts as a dehydrogenation reagent and an oxidizer in synthetic organic chemistry. In the Thiele-Winter reaction, it is involved in the preparation of triacetate of hydroxyquinol by reacting with acetic anhydride and sulfuric acid. It is also used in the synthesis of bromadol and to suppress double- bond migration during olefin metathesis reactions. It is used as a precursor to hydroquinone which finds application in photography and as a reducing agent and an antioxidant in rubber production.

Reactions

1,4-Benzoquinone and its derivatives are extensively used in Diels-Alder reactions. A facile tautomerization of alkyl substituted 1,4-benzoquinone to o-quinone methide is the highlight of this cycloaddition.Diels-Alder reaction of 1,4-benzoquinone with thiophene dioxide by Kang et al.

Synthesis Reference(s)

Chemistry Letters, 14, p. 603, 1985The Journal of Organic Chemistry, 48, p. 5160, 1983 DOI: 10.1021/jo00174a003Tetrahedron Letters, 29, p. 677, 1988 DOI: 10.1016/S0040-4039(00)80182-3

General Description

Benzoquinone appears as a yellowish-colored crystalline solid with a pungent, irritating odor. Poisonous by ingestion or inhalation of vapors. May severely damage skin, eyes and mucous membranes. Used to make dyes and as a photographic chemical.

Air & Water Reactions

Soluble in water and denser than water. If moist 1,4-Benzoquinone may decompose spontaneously above 140°F. This has occurred in drums, causing over-pressurization.

Reactivity Profile

1,4-Benzoquinone acts as an oxidizing agent .

Hazard

Toxic by inhalation, strong irritant to skin, eyes and mucous membranes. Skin damage. Ques- tionable carcinogen.

Health Hazard

1,4-Benzoquinone is moderately toxic viaingestion and skin contact. It is a mutagen andmay cause cancer. Because of its low vaporpressure, 0.1 torr (at 25°C 77°F), the healthhazard due to inhalation of its vapor is low.However, prolonged exposure may produceeye irritation, and its contact with the eyes can injure the cornea. Contact with the skincan lead to irritation, ulceration, and necrosis.The toxicity of benzoquinone is similarto that of hydroquinone and benzenetriol.Repeated intraperitoneal administration of2 mg/kg/day to rats for 6 weeks produced significantdecreases in red blood cell, bone marrowcounts, and hemoglobin content (Raoet al. 1988). In addition, relative changes inorgan weights and injuries to the liver, thymus,kidney, and spleen were observed. Lauet al. (1988) investigated the correlation oftoxicity with increased glutathione substitutionin 1,4-benzoquinone. With the exceptionof the fully substituted isomer, increased substitutionresulted in enhanced nephrotoxicity.Although the conjugates were more stable tooxidation, the toxicity increased. The oral andintravenous toxicities of this compound in ratsare as follow: LD50 value, oral (rats): 130 mg/kgLD50 value, intravenous (rats): 25 mg/kgThe carcinogenicity of 1,4-benzoquinone inhumans is not reported. However, it is amutagen. It produced tumors in the lungs andskin of mice.

Fire Hazard

Noncombustible solid; ignition can occur after only moderate heating, autoignition temperature 560°C (1040°F); fire-extinguishing agent: water spray. 1,4-Benzoquinone may react violently with strong oxidizers, especially at elevated temperatures.

Safety Profile

Poison by ingestion, subcutaneous, intraperitoneal, and intravenous routes. Questionable carcinogen with experimental tumorigenic data by skin contact. Human mutation data reported. Quinone has a characteristic, irritating odor. Causes severe damage to the skin and mucous membranes by contact with it in the solid state, in solution, or in the form of condensed vapors. Locally, it causes dlscoloration, severe irritation, erythema, swehng, and the formation of papules and vesicles, whereas prolonged contact may lead to necrosis. When the eyes become involved, it causes dangerous disturbances of vision. The moist material self-heats and decomposes exothermically above 60℃. When heated to decomposition it emits acrid smoke and fumes.

Potential Exposure

Due to this compound’s ability to react with certain nitrogen compounds to form colored sub- stances, quinone is widely used in the dye, textile, chemi- cal, tanning, and cosmetic industries. It is used as an industrial chemical; laboratory reagent; and as an interme- diate in chemical synthesis for hydroquinone and other chemicals.

Carcinogenicity

Quinone has been tested for carcinogenicity in mice by skin application or inhalation and in rats by subcutaneous injection. None of these studies were considered sufficient to evaluate carcinogenicity (335, 336). A cancer bioassay of Tribolium-infested flour has been conducted but lack of quantification of quinone and methodological issues make the data difficult to interpret. Quinone has produced negative results in studies designed to examine its ability to promote carcinogenicity. In a liver bioassay, quinone did not increase the formation of GGTpositive foci in the liver. Quinone did not promote induction of stomach or skin tumors in mice dosed with 7,12- dimethylbenzanthracene.

Environmental Fate

Quinone exists in the atmosphere in the gas phase. The dominant atmospheric loss process for quinone is expected to be by reaction with the hydroxyl (OH) radical (reaction with ozone is expected to be slow because of the >C(O) substituent groups). The estimated half-life and lifetime of quinone in the atmosphere due to reaction with the OH radical are w3 and 4 h, respectively. Release of 1,4-benzoquinone to the environment occurs via its effluents during its commercial production and use and in wastewaters from the coal industry. If released to soil, it is likely to leach (estimated Koc of 30) and may volatilize and photodegrade on soil surfaces. The ambient atmospheric concentration of 1,4-benzoquinone has been reported to be less than 15–80 ng m-3, and benzoquinone has been detected in tobacco smoke.

Shipping

UN2587 Benzoquinone, Hazard Class: 6.1; Labels: 6.1-Poisonous materials.

Purification Methods

Purify p-benzoquinone in one or more of the following ways: steam distillation followed by filtration and drying (e.g. in a desiccator over CaCl2), crystallisation from pet ether (b 80-100o), *benzene (with, then without, charcoal), water or 95% EtOH, sublimation under vacuum (e.g. from room temperature to liquid N2). It slowly decomposes and should be stored, refrigerated, in an evacuated or sealed glass vessel in the dark. It should be resublimed before use. [Wolfenden et al. J Am Chem Soc 109 463 1987, Beilstein 7 IV 2065.]

Toxicity evaluation

The acute narcotic effects are due to the physical interaction of quinone itself on the cells of the central nervous system (CNS). The long-term effects are most likely due to the production of an unstable reactive intermediate during biotransformation or redox cycling. Cytochrome P450–mediated xenobiotic metabolism often leads to biological intermediates with attributes identical to quinones.

Incompatibilities

Incompatible with oxidizers (chlorates, nitrates, peroxides, permanganates, perchlorates, chlorine, bromine, fluorine, etc.); contact may cause fires or explo- sions. Keep away from alkaline materials, strong bases, strong acids, oxoacids, epoxides, some combustible substances; reducing agents. Decomposes exothermically on warming above 60 ? C, when moist, producing carbon monoxide.

Waste Disposal

Controlled incineration (982℃, 2.0 seconds minimum).

Check Digit Verification of cas no

The CAS Registry Mumber 106-51-4 includes 6 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 3 digits, 1,0 and 6 respectively; the second part has 2 digits, 5 and 1 respectively.
Calculate Digit Verification of CAS Registry Number 106-51:
(5*1)+(4*0)+(3*6)+(2*5)+(1*1)=34
34 % 10 = 4
So 106-51-4 is a valid CAS Registry Number.
InChI:InChI=1/C6H4O2/c7-5-3-1-2-4-6(5)8/h1-4H

106-51-4 Well-known Company Product Price

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

  • (B0089)  1,4-Benzoquinone  >98.0%(T)

  • 106-51-4

  • 25g

  • 185.00CNY

  • Detail
  • TCI America

  • (B0089)  1,4-Benzoquinone  >98.0%(T)

  • 106-51-4

  • 100g

  • 510.00CNY

  • Detail
  • TCI America

  • (B0089)  1,4-Benzoquinone  >98.0%(T)

  • 106-51-4

  • 500g

  • 1,590.00CNY

  • Detail
  • TCI America

  • (B0887)  1,4-Benzoquinone  >97.0%(T)

  • 106-51-4

  • 25g

  • 130.00CNY

  • Detail
  • TCI America

  • (B0887)  1,4-Benzoquinone  >97.0%(T)

  • 106-51-4

  • 500g

  • 770.00CNY

  • Detail
  • Alfa Aesar

  • (A13162)  p-Benzoquinone, 98+%   

  • 106-51-4

  • 100g

  • 223.0CNY

  • Detail
  • Alfa Aesar

  • (A13162)  p-Benzoquinone, 98+%   

  • 106-51-4

  • 250g

  • 547.0CNY

  • Detail
  • Alfa Aesar

  • (A13162)  p-Benzoquinone, 98+%   

  • 106-51-4

  • 1000g

  • 986.0CNY

  • Detail
  • Alfa Aesar

  • (A13162)  p-Benzoquinone, 98+%   

  • 106-51-4

  • 5000g

  • 4269.0CNY

  • Detail
  • Sigma-Aldrich

  • (PHR1028)  1,4-Benzoquinone  pharmaceutical secondary standard; traceable to USP

  • 106-51-4

  • PHR1028-1G

  • 732.19CNY

  • Detail
  • Sigma-Aldrich

  • (12309)  p-Benzoquinone  for spectrophotometric det. of amines, ≥99.5% (HPLC)

  • 106-51-4

  • 12309-25G

  • 862.29CNY

  • Detail
  • Sigma-Aldrich

  • (12309)  p-Benzoquinone  for spectrophotometric det. of amines, ≥99.5% (HPLC)

  • 106-51-4

  • 12309-100G

  • 2,818.53CNY

  • Detail

106-51-4SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 10, 2017

Revision Date: Aug 10, 2017

1.Identification

1.1 GHS Product identifier

Product name 1,4-benzoquinone

1.2 Other means of identification

Product number -
Other names 2,5-Cyclohexadiene-1,4-dione

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only. Quinone is used as a chemical intermediate, a polymerization inhibitor, an oxidizing agent, a photographic chemical, a tanning agent, and a chemical reagent.
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:106-51-4 SDS

106-51-4Synthetic route

4-methoxy-phenol
150-76-5

4-methoxy-phenol

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With bis-[(trifluoroacetoxy)iodo]benzene In water; acetonitrile for 0.166667h; Ambient temperature;100%
With copper(II) nitrate/zeolite H-Y Product distribution; Further Variations:; heating mode; times; microwave irradiation;100%
With manganese dioxide impregnated with nitric acid In dichloromethane for 0.5h; Ambient temperature;96%
hydroquinone
123-31-9

hydroquinone

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With barium ferrate(VI) In benzene for 0.25h; Product distribution; Heating;100%
With benzyltrimethylammonium tribromide; sodium acetate In dichloromethane; water for 2h; Ambient temperature;100%
With bis(2,2'-bipyridyl) copper(II) permanganate In dichloromethane for 0.25h; Ambient temperature;100%
phenol
108-95-2

phenol

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With CuCl2 In acetonitrile100%
With [CuII2(μ-OH)(1,2-bis(2-(bis(2-pyridylmethyl)aminomethyl)-6-pyridyl)ethane)](ClO4)3 ; dihydrogen peroxide; triethylamine In water; acetonitrile at 50℃; for 10h; Catalytic behavior; Inert atmosphere;99%
With manganese(IV) oxide; sulfuric acid; aniline at 10℃; for 1.5h;95%
hydroquinone
123-31-9

hydroquinone

A

diphenyl-2,5 furannedicarbaldehyde 3,4
36831-87-5

diphenyl-2,5 furannedicarbaldehyde 3,4

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With barium ferrate(VI) In benzene for 0.3h; Heating;A 70%
B 100%
1,4-dimethoxybezene
150-78-7

1,4-dimethoxybezene

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With bis-[(trifluoroacetoxy)iodo]benzene In methanol; water at 20℃; for 4h;100%
With manganese dioxide impregnated with nitric acid In dichloromethane for 1.5h; Ambient temperature;93%
With Oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 1h;86%
1,4-bis(trimethylsilyloxy)benzene
2117-24-0

1,4-bis(trimethylsilyloxy)benzene

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With pyridinium chlorochromate In dichloromethane at 25℃; for 2h; Mechanism; relative reaction rate;99%
With quinolinium monofluorochromate(VI) In dichloromethane for 1h; Ambient temperature;98%
With dioxochloro(trimethylsiloxy)chromate(VI) In dichloromethane for 0.333333h; Ambient temperature;97%
4-Hydroxyacetophenone
99-93-4

4-Hydroxyacetophenone

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With 3-chloro-benzenecarboperoxoic acid In acetonitrile at 80℃; for 0.75h; Baeyer-Villiger Ketone Oxidation; regioselective reaction;99%
1,4-phenylenediamine
106-50-3

1,4-phenylenediamine

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With sodium periodate In water at 20℃; for 0.166667h;98%
With [bis(acetoxy)iodo]benzene In acetone at 20℃; for 0.166667h;90%
With sulfuric acid; manganese triacetate In water at 35℃; Rate constant; Mechanism;
With dichromate anion
With manganese(IV) oxide; sulfuric acid
benzamide
55-21-0

benzamide

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With iodobenzene; oxone; water In acetonitrile at 20℃;98%
With sodium hydrogen sulfate; [bis(acetoxy)iodo]benzene In water; acetonitrile at 20℃; for 0.5h; Time; Solvent;80%
4-Ethoxyphenol
622-62-8

4-Ethoxyphenol

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With Oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 0.5h;97%
With bis-[(trifluoroacetoxy)iodo]benzene In water; acetonitrile for 0.166667h; Ambient temperature;93%
With oxone; tetrabutylammomium bromide In water; acetonitrile at 20℃; for 1h;92%
With Oxone In water; acetonitrile at 20℃; for 17h;79%
4-methoxyacetanilide
51-66-1

4-methoxyacetanilide

A

4-methoxy-2-nitroacetanilide
119-81-3

4-methoxy-2-nitroacetanilide

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With nitric acid; silica gel In dichloromethane for 0.166667h; Product distribution; Ambient temperature;A 97%
B 2%
1,4-dimethoxybezene
150-78-7

1,4-dimethoxybezene

A

1,4-dimethoxy-2-nitrobenzene
89-39-4

1,4-dimethoxy-2-nitrobenzene

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With nitric acid; silica gel In dichloromethane for 0.0833333h; Product distribution; Ambient temperature;A 97%
B 2%
phenol
108-95-2

phenol

A

2,4,6-Trinitrophenol
88-89-1

2,4,6-Trinitrophenol

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With NO+*18-crown-6*H(NO3)2- In various solvent(s) for 2h; Nitration; Heating;A 94%
B 5%
With Zn(NO3)2*2N2O4 In ethyl acetate at 20℃; for 0.25h;A 86%
B 8%
1,4-diethoxybenzene
122-95-2

1,4-diethoxybenzene

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With Oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 1h;94%
With oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 1h;94%
With ammonium cerium(IV) nitrate In water; acetonitrile at 20℃;66%
C24H23NO5

C24H23NO5

A

C17H17NO4

C17H17NO4

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With cerium(IV) ammonium nitrate; silica gel In water; acetonitrile at 20℃;A 94%
B n/a
4-(tert-butyldimethylsilyloxy)anisole
62790-87-8

4-(tert-butyldimethylsilyloxy)anisole

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 1.5h;94%
With Oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 1.5h;79%
4-methoxyphenylacetamide
3424-93-9

4-methoxyphenylacetamide

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With iodobenzene; oxone; water In acetonitrile at 20℃;94%
With sodium hydrogen sulfate; [bis(acetoxy)iodo]benzene In water; acetonitrile at 20℃; for 0.666667h;75%
benzene
71-43-2

benzene

A

p-benzoquinone
106-51-4

p-benzoquinone

B

phenol
108-95-2

phenol

Conditions
ConditionsYield
With [CuII2(μ-OH)(1,2-bis(2-(bis(2-pyridylmethyl)aminomethyl)-6-pyridyl)ethane)](ClO4)3 ; dihydrogen peroxide; triethylamine In water; acetonitrile at 50℃; for 40h; Catalytic behavior; Inert atmosphere;A 6.8%
B 93.2%
With dihydrogen peroxide In water for 0.25h; Reagent/catalyst; Irradiation;A n/a
B 81.5%
With tetrakis(acetonitrile)copper(I) perchlorate; dihydrogen peroxide In water; acetonitrile at 25℃; for 4h; Catalytic behavior; Reagent/catalyst;A 60%
B n/a
4-amino-phenol
123-30-8

4-amino-phenol

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With K10 montmorillonite; iodic acid for 0.00833333h; microwave irradiation;93%
With Montmorillonite K10; iodic acid at 68℃; for 0.00555556h; microwave irradiation;85%
With pyridine hydrogenfluoride; sodium nitrite Product distribution; Mechanism; other substrates, various temp.;80%
C25H23NO3

C25H23NO3

A

C17H15NO2

C17H15NO2

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With cerium(IV) ammonium nitrate; silica gel In water; acetonitrile at 20℃;A 93%
B n/a
N-phenylsulphonyl-Se,Se-diphenylselenimide
52867-18-2

N-phenylsulphonyl-Se,Se-diphenylselenimide

hydroquinone
123-31-9

hydroquinone

A

benzenesulfonamide
98-10-2

benzenesulfonamide

B

diphenylselenide
1132-39-4

diphenylselenide

C

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
In toluene for 25h; Product distribution; Heating; other N-sulfonylchalcogenimides, other quinones, var. solvent and time;A 92%
B 87%
C 89%
4-n-butoxyphenol
122-94-1

4-n-butoxyphenol

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With oxone; tetrabutylammomium bromide In water; acetonitrile at 20℃; for 1h;92%
With Oxone; 4-iodophenoxyacetic acid In 2,2,2-trifluoroethanol; water at 20℃; for 0.5h;88%
With Oxone In water; acetonitrile at 20℃; for 17h;77%
C28H23NO4

C28H23NO4

A

C20H15NO3

C20H15NO3

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With cerium(IV) ammonium nitrate; silica gel In water; acetonitrile at 20℃;A 91%
B n/a
C23H18Cl2N2O5

C23H18Cl2N2O5

A

3-(2,4-dichlorophenoxy)-4-(4-nitrophenyl)azetidin-2-one

3-(2,4-dichlorophenoxy)-4-(4-nitrophenyl)azetidin-2-one

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With cerium(IV) ammonium nitrate; silica gel In water; acetonitrile at 20℃;A 91%
B n/a
C27H22N2O8

C27H22N2O8

A

C20H16N2O7

C20H16N2O7

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With cerium(IV) ammonium nitrate; silica gel In dichloromethane at 20℃;A 90%
B n/a
1-(4-(benzyloxy)phenyl)-3-hydroxy-2-phenoxypropan-1-one

1-(4-(benzyloxy)phenyl)-3-hydroxy-2-phenoxypropan-1-one

A

4-Benzyloxyphenol
103-16-2

4-Benzyloxyphenol

B

4-(benzyloxy)phenyl 3-hydroxy-2-phenoxypropanoate

4-(benzyloxy)phenyl 3-hydroxy-2-phenoxypropanoate

C

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With methanesulfonic acid; dihydrogen peroxide In water; acetonitrile at 50℃; for 6h; Flow reactor; Green chemistry;A 1%
B 8%
C 90%
C23H19NO5

C23H19NO5

4-(benzo[d][1,3]dioxol-5-yl)-3-phenoxyazetidin-2-one

4-(benzo[d][1,3]dioxol-5-yl)-3-phenoxyazetidin-2-one

B

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With ceric(IV) tetra-n-butylammonium nitrate; water In dichloromethane at 20℃; for 0.333333h; Reagent/catalyst; Solvent; Temperature;A 89%
B n/a
1-(4-methoxyphenyl)-3-hydroxy-2-(2-methoxyphenoxy)propan-1-one
92409-23-9

1-(4-methoxyphenyl)-3-hydroxy-2-(2-methoxyphenoxy)propan-1-one

A

4-methoxyphenyl 3-hydroxy-2-(2-methoxyphenoxy)propanoate

4-methoxyphenyl 3-hydroxy-2-(2-methoxyphenoxy)propanoate

B

4-methoxy-phenol
150-76-5

4-methoxy-phenol

C

p-benzoquinone
106-51-4

p-benzoquinone

Conditions
ConditionsYield
With methanesulfonic acid; dihydrogen peroxide In water; acetonitrile at 50℃; for 6h; Flow reactor; Green chemistry;A 9%
B 2%
C 89%
acetic anhydride
108-24-7

acetic anhydride

p-benzoquinone
106-51-4

p-benzoquinone

1,2,4-triacetoxybenzene
613-03-6

1,2,4-triacetoxybenzene

Conditions
ConditionsYield
With sulfuric acid at 40 - 50℃;100%
With sulfuric acid at 10 - 45℃; for 1h;97.4%
With sulfuric acid at 25 - 50℃; for 0.5h; Reagent/catalyst; Temperature;96%
cyclopenta-1,3-diene
542-92-7

cyclopenta-1,3-diene

p-benzoquinone
106-51-4

p-benzoquinone

norbornenoquinone
51175-59-8

norbornenoquinone

Conditions
ConditionsYield
In hexane; ethyl acetate at 0℃; for 3.5h; Diels-Alder Cycloaddition;100%
In methanol at -78 - 0℃; Inert atmosphere; optical yield given as %de;98%
In hexane; ethyl acetate at 0℃; for 4h; Diels-Alder reaction;97%
p-benzoquinone
106-51-4

p-benzoquinone

5,6-dichlorocyclohex-2-ene-1,4-dione
5273-62-1

5,6-dichlorocyclohex-2-ene-1,4-dione

Conditions
ConditionsYield
With sulfuryl dichloride; triethylamine In diethyl ether for 0.5h;100%
With chloroform; chlorine
With sulfuryl dichloride
p-benzoquinone
106-51-4

p-benzoquinone

hydroquinone
123-31-9

hydroquinone

Conditions
ConditionsYield
With nickel In tetrahydrofuran at 20℃; for 0.166667h; Reduction;100%
With boron trifluoride diethyl etherate; sodium iodide In acetonitrile at 0℃; for 0.0833333h;99%
With hydrazine hydrate In acetonitrile at 20℃; for 18h; Irradiation;99%
sulfure de pentamethylene
1613-51-0

sulfure de pentamethylene

p-benzoquinone
106-51-4

p-benzoquinone

2,5-dihydroxyphenylthianium perchlorate

2,5-dihydroxyphenylthianium perchlorate

Conditions
ConditionsYield
With perchloric acid In acetone at 0℃;100%
sulfure de pentamethylene
1613-51-0

sulfure de pentamethylene

p-benzoquinone
106-51-4

p-benzoquinone

1-(2,5-dihydroxyphenyl)thianium bromide
89706-15-0

1-(2,5-dihydroxyphenyl)thianium bromide

Conditions
ConditionsYield
With hydrogen bromide In acetone at 0℃;100%
cyclopenta-1,3-diene
542-92-7

cyclopenta-1,3-diene

p-benzoquinone
106-51-4

p-benzoquinone

1α,4α,4aβ,10aα,5β,8β,8aα,9aβ-octahydro-1,4:5,8-dimethanoanthracene-9,10-dione
78548-82-0

1α,4α,4aβ,10aα,5β,8β,8aα,9aβ-octahydro-1,4:5,8-dimethanoanthracene-9,10-dione

Conditions
ConditionsYield
In benzene at 40℃; for 20h;100%
In dichloromethane at 20℃; for 24h; Diels-Alder reaction;100%
In ethanol at 0℃; for 0.5h; Diels-Alder Cycloaddition;98%
thiophenol
108-98-5

thiophenol

p-benzoquinone
106-51-4

p-benzoquinone

2-(phenylthio)benzene-1,4-diol
18231-96-4

2-(phenylthio)benzene-1,4-diol

Conditions
ConditionsYield
In methanol100%
With methanol at 20℃; for 6h;99%
In methanol for 0.166667h; Ambient temperature;95%
Diphenylphosphine oxide
4559-70-0

Diphenylphosphine oxide

p-benzoquinone
106-51-4

p-benzoquinone

(2,5-dihydroxyphenyl)diphenylphosphine oxide
13291-46-8

(2,5-dihydroxyphenyl)diphenylphosphine oxide

Conditions
ConditionsYield
In toluene for 1.66667h;100%
With water In toluene at 80℃; for 12h; Inert atmosphere; Schlenk technique;98%
In toluene for 20h; Inert atmosphere; Reflux;88.1%
In toluene at 75 - 110℃; for 1h; Michael Addition; Inert atmosphere;86%
In toluene
9,10-dimethylanthracene
781-43-1

9,10-dimethylanthracene

p-benzoquinone
106-51-4

p-benzoquinone

9,10-Dimethyl-12,15-dioxo-11,12,15,16-tetrahydro-triptycen
115163-71-8

9,10-Dimethyl-12,15-dioxo-11,12,15,16-tetrahydro-triptycen

Conditions
ConditionsYield
With magnesium(II) perchlorate In acetonitrile at 24.9℃; dependence of kobs on ;100%
With magnesium(II) perchlorate In acetonitrile100%
In chloroform-d1 at 24.85℃; Quantum yield;65%
With p-benzoquinone*2thymol eutectic for 0.5h; Diels-Alder reaction;95 % Spectr.
With magnesium(II) perchlorate In [D3]acetonitrile at 24.84℃; Kinetics; Further Variations:; Reagents; Diels-Alder reaction;
diphenyl phosphorohydrazidate
33862-44-1

diphenyl phosphorohydrazidate

p-benzoquinone
106-51-4

p-benzoquinone

C18H15N2O4P

C18H15N2O4P

Conditions
ConditionsYield
In benzene at 25℃;100%
cis-3-thiabicyclo<3.3.1>nonane
20742-48-7

cis-3-thiabicyclo<3.3.1>nonane

p-benzoquinone
106-51-4

p-benzoquinone

(1R,5S)-3-(2,5-Dihydroxy-phenyl)-3-thionia-bicyclo[3.3.1]nonane; hydrogen sulfate

(1R,5S)-3-(2,5-Dihydroxy-phenyl)-3-thionia-bicyclo[3.3.1]nonane; hydrogen sulfate

Conditions
ConditionsYield
With sulfuric acid In acetone at 0℃;100%
(E)-8-Nitro-octa-1,3-diene
88888-43-1

(E)-8-Nitro-octa-1,3-diene

p-benzoquinone
106-51-4

p-benzoquinone

(4aR,5R,8aS)-5-(4-Nitro-butyl)-4a,5,8,8a-tetrahydro-[1,4]naphthoquinone

(4aR,5R,8aS)-5-(4-Nitro-butyl)-4a,5,8,8a-tetrahydro-[1,4]naphthoquinone

Conditions
ConditionsYield
In toluene at 110℃; for 15h;100%
p-benzoquinone
106-51-4

p-benzoquinone

1,4-Cyclohexanedione
637-88-7

1,4-Cyclohexanedione

Conditions
ConditionsYield
With aluminium trichloride; zinc In tetrahydrofuran for 0.4h; Ambient temperature;100%
With formic acid In toluene at 120℃; for 10h; Inert atmosphere; chemoselective reaction;57%
With hydrogen; tetra-(n-butyl)ammonium iodide In water at 110℃; under 15001.5 Torr; for 24h; chemoselective reaction;57%
With ruthenium; hydrogen at 80℃; under 37503.8 Torr; for 1h; Reagent/catalyst; Ionic liquid; chemoselective reaction;
phenyltellurotrimethylsilane
73296-31-8

phenyltellurotrimethylsilane

p-benzoquinone
106-51-4

p-benzoquinone

1,4-bis(trimethylsilyloxy)benzene
2117-24-0

1,4-bis(trimethylsilyloxy)benzene

Conditions
ConditionsYield
In tetrahydrofuran at 20℃; for 0.5h; reductive silylation;100%
p-benzoquinone
106-51-4

p-benzoquinone

(E,E)-2-pyridyldimethyl(buta-1,3-dienyl)silane
270589-03-2

(E,E)-2-pyridyldimethyl(buta-1,3-dienyl)silane

[1,4]naphthoquinone
130-15-4

[1,4]naphthoquinone

Conditions
ConditionsYield
With hydrogenchloride In water at 20℃; for 38h;100%
With hydrogenchloride In water at 20℃; for 38h; Product distribution; Further Variations:; Reagents; Solvents; Diels-Alder reaction;100%
p-benzoquinone
106-51-4

p-benzoquinone

(E,E)-2-pyridyldimethyl(3-methylbuta-1,3-dienyl)silane
270589-04-3

(E,E)-2-pyridyldimethyl(3-methylbuta-1,3-dienyl)silane

6-methyl-1,4-naphthoquinone
605-93-6

6-methyl-1,4-naphthoquinone

Conditions
ConditionsYield
With hydrogenchloride In water at 20℃; for 38h;100%
With hydrogenchloride In water at 20℃; for 38h; Diels-Alder reaction;100%
tetrafluoroboric acid

tetrafluoroboric acid

1,1'-diacetylferrocene
1273-94-5

1,1'-diacetylferrocene

p-benzoquinone
106-51-4

p-benzoquinone

1,1'-diacetylferriceniumtetra-fluoroborate

1,1'-diacetylferriceniumtetra-fluoroborate

Conditions
ConditionsYield
In diethyl ether; chloroform Dropwise addn. (Ar) of ferrocene complex in dry chloroform to org. compd. in the presence of HBF4 (Et2O) at -10°C, and stirring (1 h, room temp.) of resulting soln.; Isolation of resulting compd. by filtn. and silica gel chromy.;100%
1,3-bis(trimethylsilyl)-1,3-diaza-2-germa(II)indane
117226-57-0

1,3-bis(trimethylsilyl)-1,3-diaza-2-germa(II)indane

p-benzoquinone
106-51-4

p-benzoquinone

2C6H4(N(Si(CH3)3))2(2-)*2Ge(3+)*(OC6H4O)(2-)

2C6H4(N(Si(CH3)3))2(2-)*2Ge(3+)*(OC6H4O)(2-)

Conditions
ConditionsYield
In toluene monomer feed ratio germylene : p-benzoquinone = 4.0 : 1.0, at -78°C under Ar for 1 h; elem. anal.;100%
In tetrahydrofuran monomer feed ratio germylene : p-benzoquinone = 2.0 : 1.0, at -78°C under Ar for 1 h; elem. anal.;96%
In toluene monomer feed ratio germylene : p-benzoquinone = 2.0 : 1.0, at -78°C under Ar for 1 h; elem. anal.;91%
In toluene monomer feed ratio germylene : p-benzoquinone = 1.0 : 1.0, at -78°C under Ar for 1 h; elem. anal.;86%
bis(β-dimethylaminoethoxy)tin

bis(β-dimethylaminoethoxy)tin

p-benzoquinone
106-51-4

p-benzoquinone

Sn(OCH2CH2N(CH3)2)2(OC6H4O)

Sn(OCH2CH2N(CH3)2)2(OC6H4O)

Conditions
ConditionsYield
In benzene under N2, soln. of C6H4O2 in benzene added to Sn compd. in benzene at 22-24°C, refluxed with stirring for 2 h; ppt. filtered off, washed with benzene, dried; elem. anal.;100%
bis[bis(trimethylsilyl)amino]germanium(II)
59863-12-6

bis[bis(trimethylsilyl)amino]germanium(II)

p-benzoquinone
106-51-4

p-benzoquinone

Ge(N(Si(CH3)3)2)2OC6H4O

Ge(N(Si(CH3)3)2)2OC6H4O

Conditions
ConditionsYield
In benzene (Ar); stirring (1 h, 25°C); soln. filtn. off, drying (vac.);100%
In toluene (Ar); stirring (1 h, -78, 0 or 50°C); soln. filtn. off, drying (vac.); elem. anal.;100%
In diethyl ether (Ar); stirring (1 h, 0°C); soln. filtn. off, drying (vac.);99%
tetrakis(triphenylphosphine) palladium(0)
14221-01-3

tetrakis(triphenylphosphine) palladium(0)

p-benzoquinone
106-51-4

p-benzoquinone

[palladium(0)(triphenylphosphine)2(p-benzoquinone)]
490039-51-5, 57036-58-5

[palladium(0)(triphenylphosphine)2(p-benzoquinone)]

Conditions
ConditionsYield
In benzene under N2 atm. to suspn. Pd(PPh3)4 in benzene was added soln. benzoquinone in benzene and stirred for 30 min; soln. was concd., ether-hexane was added;100%
pine pitch

pine pitch

p-benzoquinone
106-51-4

p-benzoquinone

(4aR,4bS,7R,10aR,10bS,12R,12aR)-13-isopropyl-7,10a-dimethyl-1,4-dioxo-4,4a,5,6,6a,7,8,9,10,10a,10b,11,12,12a-tetradecahydro-1H-4b,12-ethenochrysene-7-carboxylic acid

(4aR,4bS,7R,10aR,10bS,12R,12aR)-13-isopropyl-7,10a-dimethyl-1,4-dioxo-4,4a,5,6,6a,7,8,9,10,10a,10b,11,12,12a-tetradecahydro-1H-4b,12-ethenochrysene-7-carboxylic acid

Conditions
ConditionsYield
With 3-butyl-1-methyl-1H-imidazol-3-ium hexafluorophosphate In hexane; benzene at 20℃; for 1h; Reactivity; Reagent/catalyst; Solvent; Darkness;100%
3,4-di-tert-butyl-2,5-dimethylthiophene 1-oxide
1243058-70-9

3,4-di-tert-butyl-2,5-dimethylthiophene 1-oxide

p-benzoquinone
106-51-4

p-benzoquinone

C20H28O3S

C20H28O3S

Conditions
ConditionsYield
In dichloromethane at 20℃; for 0.0833333h; Diels-Alder reaction;100%
2-bromothiophenol
6320-02-1

2-bromothiophenol

p-benzoquinone
106-51-4

p-benzoquinone

2-((2-bromophenyl)thio)benzene-1,4-diol
1310712-82-3

2-((2-bromophenyl)thio)benzene-1,4-diol

Conditions
ConditionsYield
In methanol100%
With methanol at 20℃; for 6h;93%

106-51-4Related news

Synthesis of 2-substituted hydroquinone derivatives from 1,4-Benzoquinone (cas 106-51-4) and allyl ethers08/21/2019

B-Alkylpinacolboranes, derived from rhodium-catalyzed hydroboration of allyl ethers with pinacolborane, react with 1,4-benzoquinone under acidic, oxidizing conditions, to afford, after subsequent hydrogenation, 2-substituted hydroquinones in isolated, purified yields of about 50% based on 1,4-be...detailed

106-51-4Relevant articles and documents

Effect of calcination temperature on the structure and catalytic performance of copper-ceria mixed oxide catalysts in phenol hydroxylation

Amadine, Othmane,Essamlali, Younes,Fihri, Aziz,Larzek, Mohamed,Zahouily, Mohamed

, p. 12586 - 12597 (2017)

We report on highly active CuO@CeO2 catalysts prepared by the surfactant-template method and calcined at different temperatures. Then the obtained catalysts were characterized by means of various analytical techniques. Our findings show that the BET surface area and pore volume of the CuO@CeO2 catalyst measured by N2 adsorption-desorption are decreasing with the elevation of calcination temperature. From the results of XRD and XPS, we determined the oxidation state of copper in the copper-ceria mixed oxide catalysts. The CuO@CeO2 catalysts displayed good catalytic activity for the phenol hydroxylation using H2O2 as an oxidant. Moreover, we found that the catalytic activity is improved for high calcining temperature and the optimum conditions were obtained when the catalyst CuO@CeO2 is calcined at 800 °C, which lead to higher phenol conversion of 54.62% with 92.87% of selectivity for catechol and hydroquinone. More importantly, the catalyst seems to be easily recovered by simple centrifugation. The results of catalyst recycling illustrated that the catalytic activity remained high even after five cycles with slight Cu leaching and slight loss of activity. Finally, a possible mechanism in phenol hydroxylation by H2O2 over CuO@CeO2 catalyst was also proposed.

Oxidation of Electron-Rich Arenes Using HFIP-UHP System

Llopis, Natalia,Baeza, Alejandro

, p. 6159 - 6164 (2020)

The straightforward oxidation of electron-rich arenes, namely, phenols, naphthols, and anisole derivatives, under mild reaction conditions, is described by means of the use of an environmentally benign HFIP-UHP system. The corresponding quinones or hydroxylated arenes were obtained in moderate to good yields.

Improving removal of 4-chlorophenol using a TiO2 photocatalytic system with microwave and ultraviolet radiation

Ki, Seo Jin,Jeon, Ki-Joon,Park, Young-Kwon,Jeong, Sangmin,Lee, Heon,Jung, Sang-Chul

, p. 15 - 22 (2017)

A conventional photocatalytic system is a viable tool to purify wastewaters, whereas poor degradation performance due to diverse pollutants under various conditions still leaves it behind commercial markets. This study aimed to determine the degradation e

Cocivera et al.

, p. 6598,6599 , 6601 ,6602 (1972)

The photochemistry of 4-chlorophenol in water revisited: The effect of cyclodextrins on cation and carbene reactions

Manet, Ilse,Monti, Sandra,Bortolus, Pietro,Fagnoni, Maurizio,Albini, Angelo

, p. 4274 - 4282 (2005)

The photochemistry of 4-chlorophenol (1) in water and in the presence of cyclodextrins has been studied by means of steady-state and time-resolved experiments. These have shown that 1 undergoes photoheterolysis of the C-Cl bond in the triplet state to yield the 4-hydroxyphenyl cation 32 in equilibrium with 4-oxocyclohexa-2,5-dienylidene, 33. These triplet intermediates scarcely react with a n nucleophile, such as water, nor abstract hydrogen from this solvent, thus they are long-lived (≈1 μs). Specific trapping of both intermediates has been achieved. The cation adds to 2-propenol, kadd~1.3× 108 M-1 s-1, to form the long-lived phenonium ion 11 (with λmax = 290 nm), which then converts to 3-(4-hydroxyphenyl)propane-1,2-diol (10). Carbene 33 is trapped by oxygen to give benzoquinone and is reduced by D-glucose (kq = 8.5 × 10-1 s-1) to give the phenoxyl radical (8) and phenol (9). Cyclodextrins have been found to trap the intermediates much more efficiently (kq = 9.4×10 8M-1s-1 with β-CD), which indicates that inclusion is involved. Ground state 1 forms inclusion complexes with 1:1 stoichiometry and association constants of 140 and 300 M-1 with α- and β-CD, respectively. Complexation does not change the efficiency or the mode of photofragmentation of 1; however, it does influence the course of the reaction because the major portion of the intermediates are reduced to phenol within the cavity (k′red ≥ 5 × 107 s-1) either via a radical 8 or via a radical cation 9+. Under these conditions, neither 2-propenol nor oxygen trap the intermediates to a significant extent.

Effective photodegradation of organic pollutantsin the presence of mono and bi-metallic complexes under visible-light irradiation

Chetti, Prabhakar,Gade, Ramesh,Guguloth, Venkanna,Pola, Someshwar,Ravulapelly, Koteshwar Rao,Subburu, Mahesh

, (2021)

The synthesis of new mono and bi-metallic complexes such as Zn (II) and Ag-Zn (II) complexes with organic functional group-based ligand (OFL) presented in the current work along with the exploration of their applicability in the photocatalytic degradation

Two-Dimensional Layered Zinc Silicate Nanosheets with Excellent Photocatalytic Performance for Organic Pollutant Degradation and CO2 Conversion

Wang, Lan,Bahnemann, Detlef W.,Bian, Liang,Dong, Guohui,Zhao, Jie,Wang, Chuanyi

, p. 8103 - 8108 (2019)

Two-dimensional (2D) photocatalysts are highly attractive for their great potential in environmental remediation and energy conversion. Herein, we report a novel layered zinc silicate (LZS) photocatalyst synthesized by a liquid-phase epitaxial growth route using silica derived from vermiculite, a layered silicate clay mineral, as both the lattice-matched substrate and Si source. The epitaxial growth of LZS is limited in the 2D directions, thus generating the vermiculite-type crystal structure and ultrathin nanosheet morphology with thicknesses of 8–15 nm and a lateral size of about 200 nm. Experimental observations and DFT calculations indicated that LZS has a superior band alignment for the degradation of organic pollutants and reduction of CO2 to CO. The material exhibited efficient photocatalytic performance for 4-chlorophenol (4-CP) degradation and CO2 conversion into CO and is the first example of a claylike 2D photocatalyst with strong photooxidation and photoreduction capabilities.

Electron Attachment to p-Benzoquinone and Photodetachment from Benzoquinone Anion in Nonpolar Solvents

Holroyd, R. A.

, p. 3541 - 3547 (1982)

Although p-benzoquinone has a high electron affinity (1.9 eV), its reaction with excess electrons exhibits an unusual solvent and temperature dependence.The reaction is fast and has a positive activation energy in n-pentane but is much slower and has a negative activation energy in Si(CH3)4, neopentane, and 2,2,4,4-tetramethylpentane.The results can be explained in terms of an equilibrium with a short-lived excited state of the anion: e- + benzoquinine benzoquinone(-)*.The attachment rate is fast in all solvents.The reverse, autodetachment from the excited anion, is characterized by an activation energy, which depends on the value of V0, the energy level of the electron in the liquid.For Si(CH3)4 for which V0 is the lowest (-0.55 eV), the activation energy is 5.7 kcal/mol.As V0 increases, the activation energy increases and is 9.4 kcal/mol in 2,2,4,4-tetramethylpentane for which V0=-0.35 eV.When V0 is close to zero, as in n-pentane, the activation energy is so large that detachment from the excited anion state is too slow to compete with deactivation and a fast diffusion-controlled forward rate is observed.The spectrum of benzoquinone anion as observed by the laser photodetachment technique is reported, and the threshold for photodetachment is found to be 2.32 eV in Si(CH3)4 and 2.58 eV in 2,2,4-trimethylpentane.The quantum yield of photodetachment reaches a maximum value at 480 nm in Si(CH3)4.

Kinetics and mechanism of oxidation of hydroquinone by tetrabutylammonium tribromide ion in aqueous acetic acid

Zende,Kalantre,Gokavi

, p. 1178 - 1186 (2010)

The oxidation of hydroquinone by environmentally benign tetrabutyl ammonium tribromide (TBATB) was carried out in 50% V/V aqueous acetic acid medium under pseudo-first-order conditions, keeping a large excess of hydroquinone over the oxidant. The main rea

Oxidative degradation of phenol by corona dielectric barrier discharge at gas-liquid interphase

Wang, Lei,Yu, Xin,Li, Guoxin,Li, Dailin

, p. 853 - 859 (2014)

In this study, corona gas-liquid dielectric barrier discharge reactor for phenol degradation was investigated. The discharge was formed between two needle metal electrodes and an aqueous solution surface where the counter electrode was submerged and separated by a quartz dielectric tube. Effects of solution conductivity, pH and gas composition on the degradation were examined. Experimental results showed that the degradation of phenol proceeded perfectly in a wide range of solution conductivity. In the process of degradation of phenol, ozone was additionally formed. The removal of phenol increased with the order: argon air oxygen. Increasing pH was favorable for phenol removal. When using argon as the discharge gas, the major degradation products were catechol, hydroquinone, hydroxyhydroquinone, acetic acid, formic acid and oxalic acid. In oxygen or air discharges, 1,4-benzoquinone and muconic acid were additionally formed. The energy efficiency of removal of phenol has been compared with other competitive processes.

-

Granick et al.

, p. 1802,1803 (1940)

-

DUET ELECTROSYNTHESIS OF p-BENZOQUINONE FROM BENZENE

Ito, Sotaro,Iwata, Mikio,Sasaki, Kazuo

, p. 841 - 850 (1991)

The combination of anodic oxidation of benzene using Ag(I)/Ag(II) mediator with cathodic oxidation of benzene using Cu(I)/Cu(II) mediator in a single electrolytic cell produces p-benzoquinone selectively in both anodic and cathodic chambers.

An efficient method for the oxidation of phenolic compounds using new Co(II) and Fe(II) phthalocyanines

Saka, Ece Tugba,?elik, Gonca,Sark?, Gülb?nar,Kantekin, Halit

, p. 161 - 168 (2016)

In this study novel Co(II) and Fe(II) phthalocyanines have been successfully prepared and their structural characterization have been done using with different spectroscopic methods (IR, 1H-NMR, UV–Vis, mass spectroscopies and elemental analysis). Substituted phenolic compounds as substrate, different kinds of oxidants and novel Co(II) and Fe(II) phthalocyanines as catalyst have been used in all oxidation reactions. Temperature, different oxidants, ox./cat. ratio effects on the catalysis have been determined. Interestingly, Co(II) phthalocyanine exhibits superior catalytic activity and durability in the catalysis over oxidation of p-nitrophenol (4-NP). The present method is simple, environmentally benign and amenable scale up process.

Sulfonic-functionalized MIL-101 as bifunctional catalyst for cyclohexene oxidation

Sun, Weng-Jie,Gao, En-Qing

, (2020)

Metal-organic frameworks (MOFs) are newly emerging and versatile platforms for designing catalysts, and catalytic oxidation of cyclohexene has attracted much academic and industrial attention for the versatile reactivity of the substrate and the great importance of the various oxygenated products. Here we report the bifunctional catalytic properties of a sulfonic-containing MOF, MIL-101-SO3H, for cyclohexene oxidation. The sulfonic group and the Cr(III) site acts in a complementary or collaborative way. The Cr(III) framework promotes the oxidation to 3-hydroperoxycyclohex-1-ene (perox) and 2-cyclohexen-1-one (1-one) (route A), whereas the sulfonic group in collaboration with the Cr(III) framework promotes the oxidation to diol (route B) and also enhances further conversions in route A: from perox to 1-one, to 2-cyclohexen-1,4-dione (dione) and even to benzoquinone. With the bifunctional MOF, molecular oxygen alone cannot oxidize cyclohexene but participates as oxidant cooperating with tert-butyl hydroperoxide (TBHP) to accelerate the reactions and to alter the product distribution in favor of dione.

Direct synthesis of phenol from benzene catalyzed by multi-V-POMs complex

Yang, Hua,Wu, Qing,Li, Jun,Dai, Wen,Zhang, Hengyun,Lu, Dan,Gao, Shuang,You, Wansheng

, p. 21 - 25 (2013)

A novel catalyst, [Mo2V2O9(bpy) 6][PMo11VO40], was synthesized by the self-assembling of [PMo11VO40]4- and [Mo 2V2O9(bpy)6]4+ unit and characterized by elemental analyses, TG, IR, X-ray powder diffraction and X-ray single crystal diffraction. [Mo2V2O9(bpy) 6][PMo11VO40] with multi-isolated active sites showed good catalytic activities for hydroxylation of benzene to phenol. A high yield of phenol (25.5%) with selectivity to phenol of 90.7% was obtained using H2O2 as oxidant. The catalyst can be recycled for 5 times while its structure was unchanged and its catalytic activity was maintained.

Oxidative degradation of monomeric and dimeric phenylpropanoids: Reactivity and mechanistic investigation

Canevali, Carmen,Orlandi, Marco,Pardi, Luca,Rindone, Bruno,Scotti, Roberto,Sipila, Jussi,Morazzoni, Franca

, p. 3007 - 3014 (2002)

The oxidative degradation of lignin related model compounds catalysed by [N,N'-bis(salicylidene)ethane-1,2-diaminato]cobalt(II), [Co(salen)], have been studied in chloroform. Arylglycerol β-aryl ethers, phenylcoumarans and apocynol showed very high conversion values within 30 minutes of the start of the reaction and their conversion rates were higher than those reported for phenylpropenoidic compounds, methyl (E)-ferulate and methyl (E)-4-hydroxycinnamate. The results of the CW electron paramagnetic resonance (EPR) investigation using the X-band, performed at the reaction temperature (298 K) showed that two phenoxy cobalt radicals ([CoIII(salen)(ROH)(RO·)] and [CoIII(salen)(RO-)(RO·)]) are involved in the oxidation mechanism of all the phenol compounds ROH. In a frozen solution the [CoIII(salen)(ROH))(RO·)] radical prevailed and its axial magnetic anisotropy was determined using high frequency, 190 GHz, CW EPR spectra. The X-band EPR monitoring of the phenoxy cobalt radicals during the reaction showed a faster decrease in the amounts of radical in the oxidation of propanoidic phenols compared with that of propenoidic phenols. The lifetime of the radicals formed from substrates having a methoxy group ortho to the aromatic hydroxy was also shorter than from substrates lacking this functionality. Both reactivity and spectroscopic data suggest that the lifetime of the phenoxy cobalt radicals correlates with the conversion rates of the substrates.

Application of photoactive electrospun nanofiber materials with immobilized meso-tetraphenylporphyrin for parabens photodegradation

Gmurek,Bizukoj?,Mosinger,Ledakowicz

, p. 160 - 167 (2014)

The pollution of aqueous environment by trace amounts of anthropogenic chemical substances has a hazardous impact on regular development of plants and animals as well as on human health. The paper presents the results of studies on the heterogeneous degradation of butyl- and benzylparaben in aqueous solutions using photochemically catalyzed processes. Meso-tetraphenylporphyrin (TPP) was immobilized in the polyurethane nanofiber material by electro-spinning method. The xenon lamp was used as a simulated sunlight source. The influence of various process parameters on reaction rate was investigated. The reuse of the carrier with the immobilized photosensitizer was examined. The major role of the singlet oxygen (1Δg) during the photodegradation was proved by using sodium azide and radical scavengers. The adsorption isotherms of parabens onto nanofiber material were determined using BET model. The kinetic study showed that the heterogeneous photodegradation of parabens could be modeled using Langmuir-Hinshelwood model and rate constants have been reported. The reaction pathway for the photodegradation of parabens via 1Δg was proposed.

Promoting Effect of TiO2 and Al2O3 Supports on the Activity of Vanadium Oxide Catalyst for the Oxidation of Benzene Measured in Terms of the Turnover Frequency

Inomata, Makoto,Miyamoto, Akira,Murakami, Yuichi

, p. 233 - 234 (1980)

The following relationship, V2O5-TiO2 > unsupported V2O5 > V2O5-Al2O3, was found to hold for the turnover frequency for the oxidation of benzene, which indicates the promoting effect of the TiO2 support on the reaction with vanadium oxide catalyst.

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Boontanonda,Grigg

, p. 583 (1977)

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A Chemo-Enzymatic Cascade for the Smart Detection of Nitro- and Halogenated Phenols

Watthaisong, Pratchaya,Pongpamorn, Pornkanok,Pimviriyakul, Panu,Maenpuen, Somchart,Ohmiya, Yoshihiro,Chaiyen, Pimchai

, p. 13254 - 13258 (2019)

The flavin-dependent monooxygenase, HadA, catalyzes the dehalogenation and denitration of the toxicants, nitro- and halogenated phenols, to benzoquinone. The HadA reaction can be applied in one-pot reactions towards the de novo synthesis of d-luciferin by coupling with d-Cys condensation. d-luciferin, a valuable chemical widely used in biomedical applications, can be used as a substrate for the reaction of firefly luciferase to generate bioluminescence. As nitro- and halogenated phenols are key indicators of human overexposure to pesticides and pesticide contamination, the technology provides a sensitive and convenient tool for improved biomedical and environmental detection at ppb sensitivity in biological samples without the requirement for any pre-treatment. This dual-pronged method combines the advantages of waste biodetoxification to produce a valuable chemical as well as a smart detection tool for environmental and biomedical detection.

Electron-transfer oxidation of chlorophenols by uranyl ion excited state in aqueous solution. Steady-state and Nanosecond flash photolysis studies

Sarakha, Mohamed,Bolte, Michele,Burrows, Hugh D.

, p. 3142 - 3149 (2000)

The oxidation of chlorophenols by photoexcited uranyl ion was studied in aqueous solution at concentrations where the ground-state interactions were negligible. Nanosecond flash photolysis showed that a clean electron-transfer process from the chlorophenols to the excited uranyl ion is involved. This is suggested to lead to the formation of a U(V)/chlorophenoxyl radical pair complex. The efficiency of this charge-transfer process is unity for the three chlorophenols. However, low product yields suggest that in the absence of oxygen, back electron transfer, both within the radical pair and from separated uranium(V) to phenoxyl radicals, appears to be the major reaction pathway. In the presence of oxygen the quantum yields of disappearance of chlorophenol and of photoproduct formation increased. This leads to the conclusion that oxygen favors reaction with uranium(V) and/or the uranium(V) - phenoxyl radical pair, leading to the formation of the superoxide anion and its conjugate acid, HO2*, which then regenerate UO22+. Based on this, a catalytic cycle for chlorophenol photooxidation involving uranyl ion and molecular oxygen is proposed.

Electrochemical incineration of 4-chlorophenol and the identification of products and intermediates by mass spectrometry

Johnson, Steve K.,Houk, Linda L.,Feng, Jianren,Houk,Johnson, Dennis C.

, p. 2638 - 2644 (1999)

This report summarizes results obtained as part of a larger effort to demonstrate the applicability of electrolytic procedures for the direct anodic (oxidative) degradation of toxic organic wastes. We refer to this process as "electrochemical incineration" (ECI) because the ultimate degradation products, e.g., carbon dioxide, are equivalent to those achieved by thermal incineration processes. In this work, the ECI of 4-chlorophenol is achieved in an aqueous medium using a platinum anode coated with a quaternary metal oxide film containing Ti, Ru, Sn, and Sb oxides. The electrode is stable and active when used with a solid Nafion membrane without the addition of soluble supporting electrolyte. Liquid chromatography (LC), including reverse phase and ion exchange chromatography, is coupled with electrospray mass spectrometry (ES-MS) and used, along with gas chromatography-mass spectrometry (GC-MS) and measurements of pH, chemical oxygen demand (COD), and total organic carbon (TOC), to study the reaction and identify the intermediate products from the ECI of 4-chlorophenol. Twenty-six intermediate products are identified and reported. The most abundant of these products are benzoquinone, 4-chlorocatechol, maleic acid, succinic acid, malonic acid, and the inorganic anions chloride, chlorate, and perchlorate. After 24 h of ECI, a solution that initially contained 108 ppm 4-chlorophenol yields only 1 ppm TOC with 98% of the original chlorine remaining in the specified inorganic forms. LC-ES-MS and direct infusion ES-MS detection limits are between 80 ppb and 4 ppm for these intermediate products. Elemental analysis of the electrolyzed solutions by inductively coupled plasma mass spectrometry ICP-MS showed that only trace amounts (25 ppb) of the metallic elements comprising the metal oxide film were present in the solution.

Hydrolysis of N-Acetyl-p-benzoquinone Imines: pH Dependence of the Partitioning of a Tetrahedral Intermediate

Novak, Michael,Bonham, Gayl A.,Mulero, Julio J.,Pelecanou, Maria,Zemis, Joseph N.,et al.

, p. 4447 - 4456 (1989)

The hydrolysis reactions of N-acetyl-p-benzoquinone imine, 1a, and its 3,5- and 2,6-dimethyl analogues, 1b and 1c, in the pH range 0.3-10.5 are described.At pH 6.0 the carbinolamide intermediates 2a-c can be detected by 1H NMR, UV, and HPLC methods.The pH-dependent partitioning of 2a and 2c can be monitored since the reversion of these intermediates to the protonated N-acylimines 5a and 5c leads to products of the conjugate attack of Cl(-), the 3-chloroacetaminophen derivatives 4a and 4c.A mechanism for the hydrolysis of 1a-c (Scheme I) is proposed which accurately predicts the time dependence of the formation of 2 and the final hydrolysis products, the p-benzoquinones 3, and 4.The alternative O-protonation mechanism (Scheme II) is tentatively rejected on the basis of substituent effect data.The relationship of the hydrolysis reactions of 1a-c to those of ordinary imines is discussed.

Thermodynamics of Disproportionation and Heats of Hydration of 1,4-Benzosemiquinone and 1,4-Naphthosemiquinone at pH 7.1

Alegria, Antonio E.,Munoz, Carlos,Rodriguez, Maria S.

, p. 930 - 934 (1990)

The thermodynamics of disproportionation of 1,4-benzosemiquinone (BQ*-) and 1,4-naphthosemiquinone (NQ*-) in cacodylic-cacodylate buffer at pH 7.1 was studied by spin resonance (ESR) spectroscopy and solution calorimetry.The disproportionation of BQ*- was found to be more exergonic and exothermic than that corresponding to NQ*- in both aqueous and gas phases.These semiquinones disproportionate about 40 times more exothermically in the gaseous than in the aqueous phase.The differences between the enthalpies of disproportionation corresponding to BQ*- and NQ*- are 51 and 14 kJ/mol in the gaseous and aqueous phases, respectively.The heats of hydration of BQ*- and NQ*- were determined with a convenient thermochemical cycle based on the enthalpies of disproportionation.The single-ion heats of hydration of BQ*- and NQ*- were found to be -360 and -377 kJ/mol, respectively.The heats of hydration of the net negative charge in BQ*- and NQ*- were found to be the same.

On the photocatalytic degradation of phenol and dichloroacetate by BiVO4: The need of a sacrificial electron acceptor

Castillo, Nikola C.,Ding, Laura,Heel, Andre,Graule, Thomas,Pulgarin, Cesar

, p. 221 - 227 (2010)

The photodegradation of phenol and dichloroacetic acid (DCAA) by BiVO 4 was studied in the absence as well as presence of selected electron scavengers. The experiments were performed under the visible (vis) irradiation of aqueous solutions over a wide pH range (1-13). Phenol was photocatalytically degraded by BiVO4 into p-benzoquinone below pH 3 and into an open-ring structure at pH 13. Methylene blue (MB) accelerated the reaction below the isoelectric point of BiVO4 and did not undergo significant degradation. In presence of H2O2, phenol was rapidly degraded up to pH 9. The degradation rates are two orders of magnitude higher than in absence of electron scavenger. The degradation of dichloroacetic acid was only possible in presence of H2O2. High initial concentrations of H2O2 inhibit the reaction and its consumption is very fast. Sequential additions of this sacrificial electron acceptor (SEA) enables the total degradation of a 1 mM DCAA solution.

Photocatalytic removal of benzene over Ti3C2T: XMXene and TiO2-MXene composite materials under solar and NIR irradiation

Calvino, José J.,Constantinescu, Gabriel,Frade, Jorge R.,Kovalevsky, Andrei V.,Labrincha, Jo?o A.,Lajaunie, Luc,Lopes, Daniela V.,Sergiienko, Sergii A.,Shaula, Aliaksandr L.,Shcherban, Nataliya D.,Shkepu, Viacheslav I.,Tobaldi, David M.

, p. 626 - 639 (2022/01/22)

MXenes, a family of two-dimensional (2D) transition metal carbides, nitrides and carbonitrides based on earth-abundant constituents, are prospective candidates for energy conversion applications, including photocatalysis. While the activity of individual MXenes towards various photocatalytic processes is still debatable, these materials were proved to be excellent co-catalysts, accelerating the charge separation and suppressing the exciton recombination. Titanium-containing MXenes are well compatible with the classical TiO2 photocatalyst. The TiO2 component can be directly grown on MXene sheets by in situ oxidation, representing a mainstream processing approach for such composites. In this study, an essentially different approach has been implemented: a series of TiO2-MXene composite materials with controlled composition and both reference end members were prepared, involving two different strategies for mixing sol-gel-derived TiO2 nanopowder with the Ti3C2Tx component, which was obtained by HF etching of self-propagating high-temperature synthesis products containing modified MAX phase Ti3C2Alz (z > 1) with nominal aluminium excess. The prospects of such composites for the degradation of organic pollutants under simulated solar light, using benzene as a model system, were demonstrated and analysed in combination with their structural, microstructural and optical properties. A notable photocatalytic activity of bare MXene under near infrared light was discovered, suggesting further prospects for light-to-energy harvesting spanning from UV-A to NIR and applications in biomedical imaging and sensors.

Direct catalytic benzene hydroxylation under mild reaction conditions by using a monocationic μ-nitrido-bridged iron phthalocyanine dimer with 16 peripheral methyl groups

Tanaka, Kentaro,Teoh, Chee-Ming,Toyoda, Yuka,Yamada, Yasuyuki

supporting information, p. 955 - 958 (2022/02/07)

Direct catalytic hydroxylation of benzene under mild reaction conditions proceeded efficiently in the presence of a monocationic μ-nitrido-bridged iron phthalocyanine dimer with 16 peripheral methyl groups in an acetonitrile solution with excess H2O2. Mechanistic studies suggested that the reaction was catalyzed by a high-valent iron-oxo species generated in situ. Moreover, the peripheral methyl groups of the catalyst were presumed to have enhanced the production rate of the iron-oxo species.

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