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2,4-Dichlorophenol (2,4-DCP) is a chlorinated derivative of phenol, widely recognized for its characteristic sharp, sweet, and phenolic or medicinal odor. It is an industrial chemical with a broad range of applications, serving as an intermediate in the synthesis of various agricultural and household products, including pesticides and disinfectants. Despite its economic relevance, 2,4-DCP is also known as an environmental pollutant due to its toxicity, persistence, and bioaccumulation.

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  • 120-83-2 Structure
  • Basic information

    1. Product Name: 2,4-Dichlorophenol
    2. Synonyms: Phenol, 2,4-dichloro-;4, 6-Dichlorophenol;1-Hydroxy-2,4-dichlorobenzene;NCI-C55345;2,4-Dichloro Phenol;2,4-DCP;2,4- Dichlorophenol (2,4-DCP);
    3. CAS NO:120-83-2
    4. Molecular Formula: C6H4Cl2O
    5. Molecular Weight: 163.00
    6. EINECS: 204-429-6
    7. Product Categories: N/A
    8. Mol File: 120-83-2.mol
  • Chemical Properties

    1. Melting Point: 41-44℃
    2. Boiling Point: 85.7 °C at 760 mmHg
    3. Flash Point: 10.5 °C
    4. Appearance: white to off-white crystalline solid
    5. Density: 1.383 g/cm3
    6. Vapor Density: 5.6 (vs air)
    7. Vapor Pressure: 0.136mmHg at 25°C
    8. Refractive Index: N/A
    9. Storage Temp.: N/A
    10. Solubility: N/A
    11. Water Solubility: 4.5 g/L (20℃)
    12. CAS DataBase Reference: 2,4-Dichlorophenol(CAS DataBase Reference)
    13. NIST Chemistry Reference: 2,4-Dichlorophenol(120-83-2)
    14. EPA Substance Registry System: 2,4-Dichlorophenol(120-83-2)
  • Safety Data

    1. Hazard Codes:  T:Toxic;
    2. Statements: R22:; R24:; R34:; R51/53:;
    3. Safety Statements: S26:; S36/37/39:; S45:; S61:;
    4. WGK Germany:
    5. RTECS:
    6. HazardClass: N/A
    7. PackingGroup: II
    8. Hazardous Substances Data: 120-83-2(Hazardous Substances Data)

120-83-2 Usage

Uses

Used in Agricultural Industry:
2,4-Dichlorophenol is used as a chemical intermediate for the production of pesticides, contributing to the development of effective crop protection agents.
Used in Household Products:
2,4-Dichlorophenol is used as a component in the formulation of disinfectants, helping to maintain cleanliness and hygiene in domestic settings.
Used in Environmental Remediation:
Although 2,4-Dichlorophenol is an environmental pollutant, certain bacteria can break it down, making it a potential target for bioremediation strategies to reduce its presence in air, soil, and water.
Used in Research and Development:
2,4-Dichlorophenol serves as a subject of study in environmental and health sciences, helping researchers understand its effects on human health and the environment, as well as exploring ways to mitigate its negative impacts.

Check Digit Verification of cas no

The CAS Registry Mumber 120-83-2 includes 6 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 3 digits, 1,2 and 0 respectively; the second part has 2 digits, 8 and 3 respectively.
Calculate Digit Verification of CAS Registry Number 120-83:
(5*1)+(4*2)+(3*0)+(2*8)+(1*3)=32
32 % 10 = 2
So 120-83-2 is a valid CAS Registry Number.
InChI:InChI:1S/C6H4Cl2O/c7-4-1-2-6(9)5(8)3-4/h1-3,9H

120-83-2 Well-known Company Product Price

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  • (Code)Product description
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  • Detail
  • TCI America

  • (D3865)  2,4-Dichlorophenol [for Biochemical Research]  >98.0%(GC)

  • 120-83-2

  • 1g

  • 230.00CNY

  • Detail
  • TCI America

  • (D3865)  2,4-Dichlorophenol [for Biochemical Research]  >98.0%(GC)

  • 120-83-2

  • 5g

  • 560.00CNY

  • Detail
  • Alfa Aesar

  • (A12065)  2,4-Dichlorophenol, 99%   

  • 120-83-2

  • 100g

  • 160.0CNY

  • Detail
  • Alfa Aesar

  • (A12065)  2,4-Dichlorophenol, 99%   

  • 120-83-2

  • 500g

  • 302.0CNY

  • Detail
  • Alfa Aesar

  • (A12065)  2,4-Dichlorophenol, 99%   

  • 120-83-2

  • 2500g

  • 1341.0CNY

  • Detail
  • Sigma-Aldrich

  • (07846)  2,4-Dichlorophenol  certified reference material, TraceCERT®

  • 120-83-2

  • 07846-100MG

  • 785.07CNY

  • Detail
  • Sigma-Aldrich

  • (35811)  2,4-Dichlorophenol  PESTANAL®, analytical standard

  • 120-83-2

  • 35811-1G

  • 188.37CNY

  • Detail
  • Supelco

  • (48528)  2,4-Dichlorophenol  analytical standard

  • 120-83-2

  • 000000000000048528

  • 533.52CNY

  • Detail
  • Supelco

  • (48690-U)  2,4-Dichlorophenolsolution  500 μg/mL in methanol, analytical standard

  • 120-83-2

  • 48690-U

  • 272.61CNY

  • Detail
  • Supelco

  • (40029)  2,4-Dichlorophenolsolution  5000 μg/mL in methanol, analytical standard

  • 120-83-2

  • 000000000000040029

  • 533.52CNY

  • Detail
  • USP

  • (1187954)  2,4-Dichlorophenol  United States Pharmacopeia (USP) Reference Standard

  • 120-83-2

  • 1187954-100MG

  • 4,326.66CNY

  • Detail

120-83-2SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 10, 2017

Revision Date: Aug 10, 2017

1.Identification

1.1 GHS Product identifier

Product name 2,4-dichlorophenol

1.2 Other means of identification

Product number -
Other names 2,4-DCP

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only. Intermediates
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:120-83-2 SDS

120-83-2Synthetic route

phenol
108-95-2

phenol

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With sulfuryl dichloride; diphenyl sulfide at -10℃; for 6h; Reagent/catalyst;99.5%
With hydrogenchloride; sulfuryl dichloride; diphenyl sulfide; sulfur dioxide; titanium tetrachloride at 60℃; Reagent/catalyst; Temperature; Large scale;99.5%
Stage #1: phenol With aluminum (III) chloride; Dimethyldisulphide at 50℃; for 0.333333h;
Stage #2: With chlorine Reagent/catalyst; Temperature;
99%
4-chloro-phenol
106-48-9

4-chloro-phenol

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With N-chloro-N-(benzenesulfonyl)benzenesulfonamide In acetonitrile at 20 - 25℃; for 0.25h; Green chemistry;99.2%
With 1,3-dichloro-5,5-dimethylhydantoin; diisopropylamine hydrochloride In toluene at 0℃; for 4h; Darkness; regioselective reaction;93%
Stage #1: 4-chloro-phenol In acetonitrile at 80℃; for 0.166667h;
Stage #2: With N-chloro-succinimide In acetonitrile at 80℃; for 8h; regioselective reaction;
76%
(2,4-dichlorophenoxy)trimethylsilane
17878-30-7

(2,4-dichlorophenoxy)trimethylsilane

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With (Ppyz)Zr(BH4)2Cl2 In diethyl ether for 2h; Heating;98%
With 1,4-diazabicyclo[2.2.2]octane tribromide supported on magnetic Fe3O4 nanoparticles In methanol at 20℃; for 0.0833333h;95%
With caro's acid; silica gel In dichloromethane at 20℃; for 0.666667h;90%
With nano magnetic sulfated zirconia (Fe3O4 at ZrO2/SO42-) In neat (no solvent) at 20℃; for 1.33333h; Green chemistry;82%
2,4-dichlorophenylboronic acid
68716-47-2

2,4-dichlorophenylboronic acid

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With urea hydrogen peroxide adduct In methanol at 27 - 29℃; for 0.0833333h; Temperature; Solvent; Green chemistry; chemoselective reaction;95%
With LACTIC ACID; dihydrogen peroxide In water at 20℃; for 0.25h; Reagent/catalyst; Green chemistry;93%
With potassium hydroxide In dimethyl sulfoxide at 100℃; for 0.0833333h; Microwave irradiation; Green chemistry;91%
2-(2,4-Dichlorphenoxy)-3,4,5,6-tetrahydro-2H-pyran
55962-02-2

2-(2,4-Dichlorphenoxy)-3,4,5,6-tetrahydro-2H-pyran

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With 1,4-diazabicyclo[2.2.2]octane tribromide supported on magnetic Fe3O4 nanoparticles In methanol at 20℃; for 0.0833333h;95%
1,3-dichloro-4-methoxybenzene
553-82-2

1,3-dichloro-4-methoxybenzene

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With L-Selectride In tetrahydrofuran at 67℃; for 24h;93%
Multi-step reaction with 3 steps
1: Cl2
2: NaI
3: 66 percent / CH2Cl2 / Ambient temperature
View Scheme
Multi-step reaction with 3 steps
1: Cl2
2: NaI
3: 45 percent / CH2Cl2 / Ambient temperature
View Scheme
Multi-step reaction with 3 steps
1: Cl2
2: NaI
3: 75 percent / CH2Cl2 / Ambient temperature
View Scheme
Multi-step reaction with 2 steps
1: Cl2
2: 75 percent / CH2Cl2 / Ambient temperature
View Scheme
2,4-dichlorophenyl benzoate
7396-91-0

2,4-dichlorophenyl benzoate

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With 1-methyl-pyrrolidin-2-one; potassium carbonate; thiophenol for 0.25h; Hydrolysis; debenzoylation; Heating;74%
C11H12Cl2O

C11H12Cl2O

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With 12-TPA/SBA 15 In 1,4-dioxane at 110℃;72%
1,3-dichloro-4-(4,4,5,5-tetramethyl-1,3,2-dioxaborolan-2-yl)benzene

1,3-dichloro-4-(4,4,5,5-tetramethyl-1,3,2-dioxaborolan-2-yl)benzene

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With sodium hydroxide; hydroxylamine hydrochloride In ethanol at 20℃; for 23h;69%
1,3-Dichlorobenzene
541-73-1

1,3-Dichlorobenzene

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With (difluoroboryl)dimethylglyoximatocobalt(II) bis(acetonitrile); water; 3-cyano-1-methylquinolinium cation In acetonitrile at 20℃; for 5h; Inert atmosphere; Irradiation; Green chemistry;69%
With water; lithium perchlorate; acetic acid; 2,3-dicyano-5,6-dichloro-p-benzoquinone In acetonitrile for 48h; Irradiation; Inert atmosphere; Electrolysis; chemoselective reaction;69%
With (difluoroboryl)dimethylglyoximatocobalt(II) bis(acetonitrile); water; 3-cyano-1-methylquinolinium perchlorate In acetonitrile at 20℃; for 5h; Inert atmosphere; Irradiation;
Multi-step reaction with 3 steps
1: phosphoric acid / 5 h / 50 °C / 4500.45 Torr / Autoclave
2: sodium carbonate; oxygen / 110 °C / 3750.38 Torr
3: macroporous sulfonic acid resin (pore size 1.5mm) / [(2)H6]acetone / 2.5 h / 60 °C
View Scheme
phenol
108-95-2

phenol

A

2-monochlorophenol
95-57-8

2-monochlorophenol

B

4-chloro-phenol
106-48-9

4-chloro-phenol

C

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With iron(III) chloride; diphenyl sulfide; boric acid at 30 - 70℃;A 19.5%
B 66.06%
C 10.96%
With sulfuryl dichloride; diethyl ether In dichloromethane Title compound not separated from byproducts;A 31.1%
B 65.8%
C 2.1%
With oxygen; silica gel; copper dichloride at 175℃; Product distribution; Further Variations:; Temperatures;A 4.04%
B 0.887%
C 0.201%
[bis(acetoxy)iodo]benzene
3240-34-4

[bis(acetoxy)iodo]benzene

2,4-dichloro-α-iodoanisole
106262-00-4

2,4-dichloro-α-iodoanisole

A

2,4-dichlorophenoxymethyl acetate
106262-06-0

2,4-dichlorophenoxymethyl acetate

B

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
In dichloromethane Ambient temperature;A 8%
B 66%
phenol
108-95-2

phenol

A

2,6-Dichlorophenol
87-65-0

2,6-Dichlorophenol

B

4-chloro-phenol
106-48-9

4-chloro-phenol

C

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With hydrogenchloride; sodium chlorate In water; acetic acid at 20℃; for 72h;A 4%
B 16%
C 65%
methanol
67-56-1

methanol

1,2,4-Trichlorobenzene
120-82-1

1,2,4-Trichlorobenzene

A

2,5-dichlorophenol
583-78-8

2,5-dichlorophenol

B

3,4-dichlorophenol
95-77-2

3,4-dichlorophenol

C

1,3-dichloro-4-methoxybenzene
553-82-2

1,3-dichloro-4-methoxybenzene

D

2,5-dichloroanisole
1984-58-3

2,5-dichloroanisole

E

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

F

3,4-dichloroanisole
36404-30-5

3,4-dichloroanisole

Conditions
ConditionsYield
With water; sodium hydroxide at 190℃; for 1.5h; Autoclave;A 64.6%
B n/a
C n/a
D n/a
E n/a
F n/a
With water; sodium hydroxide at 190℃; for 1.5h; Sealed tube; regioselective reaction;
phenol
108-95-2

phenol

A

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

B

2,4,6-Trichlorophenol
88-06-2

2,4,6-Trichlorophenol

Conditions
ConditionsYield
With hydrogenchloride; sodium chlorate In water; acetic acid at 20℃; for 26h;A 6%
B 60%
Multi-step reaction with 2 steps
1.1: Cu-Mn spinel oxide / acetonitrile / 0.17 h / 80 °C
1.2: 10 h / 80 °C
2.1: N-chloro-succinimide / 10 h / 80 °C
View Scheme
Multi-step reaction with 2 steps
1.1: Cu-Mn spinel oxide / acetonitrile / 0.17 h / 80 °C
1.2: 10 h / 80 °C
2.1: N-chloro-succinimide / 10 h / 80 °C
View Scheme
Multi-step reaction with 2 steps
1.1: Cu-Mn spinel oxide / acetonitrile / 0.17 h / 80 °C
1.2: 8 h / 80 °C
2.1: N-chloro-succinimide / 10 h / 80 °C
View Scheme
Multi-step reaction with 2 steps
1: N-chloro-succinimide / 10 h / 80 °C
2: N-chloro-succinimide / 10 h / 80 °C
View Scheme
phenol
108-95-2

phenol

A

2,6-Dichlorophenol
87-65-0

2,6-Dichlorophenol

B

2-monochlorophenol
95-57-8

2-monochlorophenol

C

4-chloro-phenol
106-48-9

4-chloro-phenol

D

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

E

2,4,6-Trichlorophenol
88-06-2

2,4,6-Trichlorophenol

Conditions
ConditionsYield
With aluminium trichloride; diphenyl sulfide; chlorine In neat (no solvent) at 35℃; for 1.5h; Product distribution; others 2-alkylphenols; var. chlorinating agent, temp., and time;A 0.5%
B 18.4%
C 58.6%
D 7.7%
E 0.5%
With N,N'-dichloropiperazine; silica gel In tetrachloromethane at 25℃; Product distribution; further reagents;
With tert-butylhypochlorite; tris(3-pyridiniumprop-1-yl)benzene-1,3,5-tricarboxylatetrichloride In acetonitrile Product distribution; Mechanism; other tentacle reagents and variations of concentration;
With tert-butylhypochlorite; cetylpyridinium chloride In water Product distribution; other reagents and solvent;
With sulfuryl dichloride; 2-aminopyridine In toluene at 70℃; for 1h; Product distribution; chlorination catalyzed by var. amines under var. conditions;A n/a
B 32.3 % Chromat.
C 60.3 % Chromat.
D n/a
E n/a
2,4-Dichlorophenoxyacetic acid
94-75-7

2,4-Dichlorophenoxyacetic acid

A

2-monochlorophenol
95-57-8

2-monochlorophenol

B

4-chloro-phenol
106-48-9

4-chloro-phenol

C

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

D

7-chloro-benzo[1,4]dioxin-2-one
329219-99-0

7-chloro-benzo[1,4]dioxin-2-one

Conditions
ConditionsYield
With air In water for 7h; Product distribution; Ambient temperature; Irradiation; also under argon atmosphere; photodegradation pathways;A 5%
B 26%
C 58%
D 5%
2,4-dichloro-α-iodoanisole
106262-00-4

2,4-dichloro-α-iodoanisole

propionyloxy>iodo>benzene

propionyloxy>iodo>benzene

A

iodobenzene
591-50-4

iodobenzene

B

2,4-dichlorophenoxymethyl 2-propionate
106262-03-7

2,4-dichlorophenoxymethyl 2-propionate

C

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
In dichloromethane for 6h; Ambient temperature;A n/a
B 54%
C n/a
phenol
108-95-2

phenol

A

2,6-Dichlorophenol
87-65-0

2,6-Dichlorophenol

B

2-monochlorophenol
95-57-8

2-monochlorophenol

C

4-chloro-phenol
106-48-9

4-chloro-phenol

D

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With chloroamine In water pH=9.0; Product distribution; Further Variations:; Reagents; pH-values;A 9.6%
B 50.5%
C 23%
D 16.3%
With oxygen; silica gel; copper dichloride at 200℃; Formation of xenobiotics;A 0.004%
B 4.761%
C 1.149%
D 0.393%
With oxygen; silica gel; copper dichloride at 225℃; Formation of xenobiotics; Further byproducts.;A 0.008%
B 3.892%
C 0.998%
D 0.394%
2,4-dichloro-α-iodoanisole
106262-00-4

2,4-dichloro-α-iodoanisole

benzene

benzene

A

iodobenzene
591-50-4

iodobenzene

B

2,4-dichlorophenoxymethyl p-bromophenoxyacetate
106262-02-6

2,4-dichlorophenoxymethyl p-bromophenoxyacetate

C

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
In dichloromethane for 6h; Ambient temperature;A n/a
B 47%
C n/a
3,5-dichlorosalicyclaldehyde
90-60-8

3,5-dichlorosalicyclaldehyde

A

3,5,3',5'-tetrachloro-2,2'-dihydroxy-benzophenone
4936-94-1

3,5,3',5'-tetrachloro-2,2'-dihydroxy-benzophenone

B

2,4-dichlorophenol
120-83-2

2,4-dichlorophenol

Conditions
ConditionsYield
With dicarbonyl(acetylacotonato)rhodium(I); copper(II) acetate monohydrate; sodium carbonate In N,N-dimethyl-formamide at 100℃; for 24h; Schlenk technique; Inert atmosphere;A 46%
B 10%

120-83-2Related news

Efficient remediation of 2,4-Dichlorophenol (cas 120-83-2) from aqueous solution using β-cyclodextrin-based submicron polymeric particles09/06/2019

The water contamination by 2,4-dichlorophenol (2,4-DCP) is a tough environmental problem, so its removal has aroused much attention recently. In this study, the synthesis of a β-cyclodextrin-based submicron polymeric particles (CSPs) is described along with its utilization as adsorbent for the ...detailed

Degradation of 2,4-Dichlorophenol (cas 120-83-2) by a novel iron based system and its synergism with Cd(II) immobilization in a contaminated soil09/05/2019

Nowadays, the remediation of heavy metals and organic compounds contaminated soil has been greatly growing attentions. In this paper, the feasibility of a novel biochar-supported zero valent iron (B-nZVI) based system for the degradation of 2,4-Dichlorophenol (2,4-DCP) and immobilization of Cd(I...detailed

A highly sensitive and selective electrochemical sensor based on polydopamine functionalized graphene and molecularly imprinted polymer for the 2,4-Dichlorophenol (cas 120-83-2) recognition and detection09/04/2019

In this work, a sensitive and selective electrochemical sensor based on polydopamine-reduced graphene oxide (PDA-rGO) and molecular imprinted polymers (MIP) modified glassy carbon electrode for detection of 2,4-DCP was fabricated. The PDA-rGO was obtained through the auto polymerization of dopam...detailed

Organic-inorganic nanocomposites fabricated via functional ionic liquid as the bridging agent for Laccase immobilization and its application in 2,4-Dichlorophenol (cas 120-83-2) removal08/31/2019

In this study, organic-inorganic nanocomposite including mesoporous silica SBA-15 and chitosan was combined using carboxyl-functionalized ionic liquid as the bridging agent (SBA-CIL-CS), and which was characterized by scanning electron microscope, Fourier transform infrared spectroscopy, thermog...detailed

Heterogeneous activation of peroxymonocarbonate by chalcopyrite (CuFeS2) for efficient degradation of 2,4-Dichlorophenol (cas 120-83-2) in simulated groundwater08/30/2019

Recently, increasing attention has been paid to the activated peroxymonocarbonate (APMC) process, because it is envisioned to be engineered for the chemical oxidation remediation of groundwater in karstic regions with elevated levels of naturally occurring bicarbonate. In the present study, we e...detailed

Biological treatment of high strength ammonia wastewater containing 2,4-Dichlorophenol (cas 120-83-2) in a membrane bioreactor: System performance and microbial community08/29/2019

Two membrane bioreactors (toxic MBR and blank MBR) were established and compared to treat high ammonia wastewater in the presence and absence of 2,4-dichlorophenol (2,4-DCP). After 130 days operation, both MBRs expressed NH4+-N removal efficiency (>95%) and 2,4-DCP removal efficiency was (96.47 ...detailed

Understanding the electrode reaction process of dechlorination of 2,4-Dichlorophenol (cas 120-83-2) over Ni/Fe nanoparticles: Effect of pH and 2,4-Dichlorophenol (cas 120-83-2) concentration08/28/2019

Herein, with the exploitation of iron and nickel electrodes, the 2,4-dichlorophenol (2,4-DCP) dechlorinating processes at the anode and cathode, respectively, were separately studied via various electrochemical techniques (e.g., Tafel polarization, linear polarization, electrochemical impedance ...detailed

120-83-2Relevant articles and documents

Electrooxidation of phenol on a Ti/RuO2 anode: Effect of some electrolysis parameters

Dos Santos, Iranildes D.,Afonso, Ju?lio C.,Dutra, Achilles J. B.

, p. 875 - 883 (2011)

The influences of electrolysis time, anodic area, current density and supporting electrolyte on phenol and its byproducts degradation on a Ti/RuO 2 anode were investigated. It was observed that phenol and its byproducts were rapidly broken down in the presence of chloride ions. Gas chromatography/mass spectrometry (GC/MS) data have shown that the presence of chloride ions lead to chlorophenols formation, due to reactions with Cl 2. and/or OCl generated during electrolysis. However, these intermediate products were also degraded later by the oxidizing agents. The standards established by the CONAMA (Brazilian National Council for the Environment) for phenols and chlorophenols in effluents were achieved after 360 min of electrolysis with a current density of 10 mA cm-2. Cyclic voltammograms obtained with the anodes before and after 436 h of electrolysis under severe salinity conditions (2 mol L-1) and current density (800 mA cm-2) showed that Ti/RuO2 did not lose its electrocatalytic properties. This fact indicates that Ti/RuO2 can be used for the treatment of effluents containing phenols in a chloride environment.

Rh-catalyzed direct synthesis of 2,2′-dihydroxybenzophenones and xanthones

Rao, Maddali L. N.,Ramakrishna, Boddu S.

, p. 75505 - 75511 (2016)

An efficient rhodium-catalyzed direct synthesis of 2,2′-dihydroxybenzophenones and xanthones was developed from functionalized salicylaldehydes. This approach provides an easy access to various functionalized 2,2′-dihydroxybenzophenone and xanthone core s

Spectral and GC-MS analysis of phototransformation of herbicides in water

Chaikovskaya,Sokolova,Karetnikova,Mal'Kov,Kuz'Mina

, p. 396 - 401 (2009)

The phototransformation of 2,4-dichlorophenoxyacetic and 2-methyl-4-chlorophenoxyacetic acids in water was studied using the KrCl*(λrad 222 nm) and XeBr*(λrad 283 nm) excilamps as UV radiation source.

Kinetics of heterogeneous photocatalytic decomposition of 2,4-dichlorophenoxyacetic acid over titanium dioxide and zinc oxide in aqueous solution

Djebbar,Sehili

, p. 269 - 276 (1998)

The photocatalytic transformation of 2,4-D in aqueous solution containing a suspension of titanium dioxide or zinc oxide leads to the formation of intermediates which are totally mineralised to carbon dioxide and hydrogen chloride (2,4-dichlorophenol and chlorohydroquinone are the major intermediates). The products at the initial stage of the reaction were 2,4-dichlorophenol (2,4-DCP), chlorohydroquinone, 4-chloropyrocatechol, 2,4-dichloro-pyrocatechol and 1.4-chlorobenzoquinone. The initial rate of photodegradation was studied as a function of the initial concentration of reactants by the linearised form of the Langmuir-Hinshelwood equation, by which rate constants κ and equilibrium adsorption constants K were evaluated. These constants were calculated at different temperatures between 25 and 60°C. The photodegradation rate increased with increase of pH. The photocatalytic transformation of 2,4-D over titanium dioxide or zinc oxide in solution containing hydrogen peroxide was studied. The latter accelerated the reaction rate of 2,4-D significantly. It was found that chloride or bicarbonate ions slowed down the photo-degradation rate of 2,4-D by scavenging hydroxyl radicals. Partial inhibition by ethanol is attributed to scavenging of the OH radicals involved in the first step of the reaction.

Frequent occurrence of triclosan hydroxylation in mammals: A combined theoretical and experimental investigation

Zhang, Hongna,Sanidad, Katherine Z.,Zhu, Lin,Parsonnet, Julie,Haggerty, Thomas D.,Zhang, Guodong,Cai, Zongwei

, (2021)

Triclosan (TCS) is a widespread antimicrobial agent with many adverse health risks. Its hepatoxicity invariably points to the activation of constitutive androstane receptor (CAR), which regulates cytochrome P450 (CYP) genes that are critical for oxidative metabolism. Here, we provide the theoretical and experimental evidences showing that metabolic activation of TCS frequently occurs through aromatic hydroxylation in mammals. CYP-mediated oxidation was predicted to take place at each aromatic C?H bond. Molecular docking and in vitro approaches reveal oxidative reaction could be efficiently catalyzed by CAR-regulated CYP2B6 enzyme. Parallel reaction monitoring (PRM) high-resolution mass spectrometry was utilized to identify and profile TCS oxidative metabolites in paired mouse liver, bile, feces, plasma and urine. We found multiple hydroxylated isomers including the products generated via the NIH shift of chlorine, as well as their subsequent conjugates. These metabolites showed isomer-specific retention in mice. Glucuronide conjugates are more readily excreted than the sulfates. Moreover, for the first time, isomeric hydroxylated metabolites were detected in the urine and stool of human subjects used TCS-contained household and personal care products. Collectively, these findings suggest that hydroxylation is an important, yet often underestimated element that worth considering to fully evaluate the biological fates and health risks of TCS.

Rate enhancement by cations in supercritical water oxidation of 2- chlorophenol

Lin, Kuen-Song,Wang, H. Paul

, p. 3278 - 3280 (1999)

Interactions between cations and Cl species in the supercritical water oxidation (SCWO) of 2.-chlorophenol (2CP) has been investigated in a high- pressure quartz-lined reactor at 673-773 K. Experimentally, we found that the S/D ratio (defined as the amount of 2CP converted to CO2 and H2O/disappearance of 2CP) for SCWO of 2CP was enhanced by cations (such as Li+, Na+, K+, Ca2+, Fe2+, or Fe3+). The S/D ratio increased as the charge density of cations increased (Fe3+> Fe2+ > Li+ > Ca2+ > Na+ > K+). Due to the extremely low solubility of metal salts in the supercritical water, abstraction of Cl in 2CP via an intermediate ((OH)PhCl(δ-)---- M(δ+) was postulated. Formation of these metal chloride (such as KCl, CaCl2, and FeCl3) precipitates in the SCWO of 2CP were identified by X-ray diffraction (XRD) spectroscopy. Since the formation of toxic highly chlorinated phenols and heavy polycyclic aromatic hydrocarbons (PAHs) was notably reduced, abstraction of Cl of 2CP by cations may occur in the early stage of the SCWO process. Interactions between cations and Cl species in the supercritical water oxidation (SCWO) of 2-chlorophenol (2CP) has been investigated in a high-pressure quartz-lined reactor at 673-773 K. Experimentally, we found that the S/D ratio (defined as the amount of 2CP converted to CO2 and H2O/disappearance of 2CP) for SCWO of 2CP was enhanced by cations (such as Li+, Na+, K+, Ca2+, Fe2+, or Fe3+). The S/D ratio increased as the charge density of cations increased (Fe3+>Fe2+>Li+>Ca2+ >Na+>K+). Due to the extremely low solubility of metal salts in the supercritical water, abstraction of Cl in 2CP via an intermediate ((OH)PhClδ-- - - - -Mδ+) was postulated. Formation of these metal chloride (such as KCl, CaCl2, and FeCl3) precipitates in the SCWO of 2CP were identified by X-ray diffraction (XRD) spectroscopy. Since the formation of toxic highly chlorinated phenols and heavy polycyclic aromatic hydrocarbons (PAHs) was notably reduced, abstraction of Cl of 2CP by cations may occur in the early stage of the SCWO process.

Sensitized photooxidation of triclosan pesticide. A kinetic study in presence of vitamin B2

Reynoso, Agustina,Possetto, David,De Gerónimo, Eduardo,Aparicio, Virginia C.,Natera, José,Massad, Walter

, (2021)

Kinetic and mechanistic aspects of Riboflavin (Rf, vitamin B2)-sensitized photochemical degradation of Triclosan (TCS) have been studied by time-resolved and stationary techniques. TCS is a broadly-used biocide, also employed in a series of industrial products as a multifunctional additive. Rf, in the presence of light and oxygen, generates singlet molecular oxygen (O2(1Δg)) and superoxide radical anion (O2[rad]–). Results indicate that TCS quenches the triplet excited state of Rf (3Rf*), O2(1Δg), and O2[rad]–. The reactive rate constant for the interaction TCS-O2(1Δg) is 62-faster in alkaline medium with respect to pH 7. Photosensitized degradation of TCS by Rf was much faster than for phenol, a model pollutant, in similar conditions of pH. Kinetic analysis indicated that the reaction of TCS with 3Rf* and/or O2[rad]– is the prevailing oxidative route. Based on the environmental importance of the TCS, the products were determined by UHPLC-MS / MS analysis.

The role of UV-irradiation pretreatment on the degradation of 2,4-dichlorophenoxyacetic acid in water

Tchaikovskaya,Sokolova,Mayer,Karetnikova,Lipatnikova,Kuzmina,Volostnov

, p. 156 - 161 (2011)

The degradation of 2,4-dichlorophenoxyacetic acid (2,4-D) in water by the combination process of UV-irradiation, humic acids and activated sludge treatment has been studied. The photoreaction rate of all irradiated samples was lowest for the sample irradiated at 308 nm (the XeCl excilamp) in the absence and in the presence of humic acids, and highest for the sample irradiated at 222 nm (the KrCl excilamp). Photolysis of 2,4-D has been shown to enhance the subsequent microbial degradation. Copyright

2,4-dichlorophenoxyacetic acid detection using 2,4- dichlorophenoxyacetic acid α-ketoglutarate dioxygenase

Yongxiang Gu,Knaebel,Korus,Crawford

, p. 1622 - 1627 (1995)

2,4-dichlorophenoxyacetic acid (2,4-D) is possibly the most widely used herbicide. Although not very toxic, cleanup of an inadvertant spill is still necessary. This phenoxy herbicide is degraded by several micro-organisms and bioremediation processes have been proposed. Analytical support for these cleanup techniques usually involves gas chromatography or immunoassays, which are moderately (ELISA assays) to very (GC/MS) expensive. Therefore, it is important to develop a quick, inexpensive, and easy-to-use 2,4-D detection method for use in the field by nonspecialists. Reported here is the construction of a detection plasmid, its introduction into Escherichia coli DH5α, and the application of cell-free extracts of this organism to highly specific 2,4-D detection. -from Authors

Synthesis of nitrogen-doped ZnO by sol-gel method: Characterization and its application on visible photocatalytic degradation of 2,4-D and picloram herbicides

Macías-Sánchez,Hinojosa-Reyes,Caballero-Quintero,De La Cruz,Ruiz-Ruiz,Hernández-Ramírez,Guzmán-Mar

, p. 536 - 542 (2015)

In this work, nitrogen-doped ZnO material was synthesized by the sol-gel method using zinc acetate as the precursor and urea as the nitrogen source (15, 20, 25 and 30% wt.). For comparative purposes, bare ZnO was also prepared. The influence of N doping on structural, morphological, optical and photocatalytic properties was investigated. The synthesized catalysts were characterized by XRD, SEM-EDS, diffuse reflectance UV-Vis spectroscopy, BET and XPS analysis. The photocatalytic activity of N-doped ZnO catalysts was evaluated during the degradation of a mixture of herbicides (2,4-D and picloram) under visible radiation ≥400 nm. The photo-absorption wavelength range of the N-doped ZnO samples was shifted to longer wavelength compared to those of the unmodified ZnO. Among different amounts of dopant agent, the 30% N-doped ZnO material showed higher visible-light activity compared with pure ZnO. Several degradation by-products were identified by using HPLC and ESI-MS/MS. The enhancement of visible photocatalytic activity of the N-doped ZnO semiconductor could be mainly due to their capability in reducing the electron-hole pair recombination. This journal is

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