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58-90-2

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58-90-2 Usage

General Description

2,3,4,6-Tetrachlorophenol is a chlorinated phenolic compound that is commonly used as a wood preservative and fungicide. It is a white crystalline solid with a strong, characteristic odor. 2,3,4,6-Tetrachlorophenol is considered highly toxic to humans and animals, and exposure can cause irritation to the skin, eyes, and respiratory tract. It is also a known environmental pollutant, and its use has been heavily regulated in many countries due to its potential harmful effects on the environment and human health. The compound is persistent in the environment and can bioaccumulate in the food chain, posing a risk to wildlife and ecosystems.

Check Digit Verification of cas no

The CAS Registry Mumber 58-90-2 includes 5 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 2 digits, 5 and 8 respectively; the second part has 2 digits, 9 and 0 respectively.
Calculate Digit Verification of CAS Registry Number 58-90:
(4*5)+(3*8)+(2*9)+(1*0)=62
62 % 10 = 2
So 58-90-2 is a valid CAS Registry Number.
InChI:InChI=1/C6H2Cl4O/c7-2-1-3(8)6(11)5(10)4(2)9/h1,11H

58-90-2 Well-known Company Product Price

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  • Sigma-Aldrich

  • (45907)  2,3,4,6-Tetrachlorophenolsolution  100 μg/mL in methanol, PESTANAL®, analytical standard

  • 58-90-2

  • 45907-2ML

  • 585.00CNY

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  • Supelco

  • (442282)  2,3,4,6-Tetrachlorophenol  analytical standard

  • 58-90-2

  • 000000000000442282

  • 703.17CNY

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  • Supelco

  • (48264)  2,3,4,6-Tetrachlorophenolsolution  certified reference material, 5000 μg/mL in methanol

  • 58-90-2

  • 000000000000048264

  • 533.52CNY

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58-90-2SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 18, 2017

Revision Date: Aug 18, 2017

1.Identification

1.1 GHS Product identifier

Product name 2,3,4,6-Tetrachlorophenol

1.2 Other means of identification

Product number -
Other names 2,3,4,6-TETRACHLOROPHENOL

1.3 Recommended use of the chemical and restrictions on use

Identified uses For industry use only.
Uses advised against no data available

1.4 Supplier's details

1.5 Emergency phone number

Emergency phone number -
Service hours Monday to Friday, 9am-5pm (Standard time zone: UTC/GMT +8 hours).

More Details:58-90-2 SDS

58-90-2Relevant articles and documents

Photocatalytic degradation of lindane by polyoxometalates: Intermediates and mechanistic aspects

Antonaraki,Triantis,Papaconstantinou,Hiskia

experimental part, p. 119 - 124 (2010/08/22)

The photocatalytic degradation of lindane (γ-1,2,3,4,5,6-hexachlorocyclohexane) has been studied in the presence of the polyoxometalate PW12O403- in aqueous solutions. Lindane is fully decomposed to CO2, Cl- and H2O, while a great variety of intermediates has been detected using GC-MS, including aromatic compounds (dichlorophenol, trichlorophenols, tetrachlorophenol, hexachlorobenzene, di- and trichloro-benzenodiol), non-aromatic cyclic compounds (penta-, tetrachlorocyclohexene, heptachlorocyclohexane), aliphatic compounds (tetrachloroethane) and condensation products (polychlorinated biphenyls). The number and nature of the intermediates implies that the mechanism of decomposition of lindane is based on both oxidative and reductive processes. Common intermediates have been reported during photolysis of lindane in the presence of titanium dioxide. A similar overall mechanism of polyoxometalates and TiO2 photocatalysis through the formation of common reactive species is suggested.

Method for reducing microcontaminants during synthesis of pentachlorophenol

-

Page/Page column 5, (2008/06/13)

A method for reducing contaminants during synthesis of pentachlorophenol includes providing a phenol-based starting material and a catalyst, which form a reaction mixture. A chlorine flow is introduced so that it is in contact with the reaction mixture, and the starting material and chlorine are reacted via a temperature-programmed reaction. The chlorine flow is terminated at a predetermined temperature prior to an end of the temperature-programmed reaction and/or at a point where the yield of pentachlorophenol is less than about 95%.

Identification of surrogate compounds for the emission of PCDD/F (I-TEQ value) and evaluation of their on-line realtime detectability in flue gases of waste incineration plants by REMPI-TOFMS mass spectrometry

Blumenstock,Zimmermann,Schramm,Kettrup

, p. 507 - 518 (2007/10/03)

Correlations between products of incomplete combustion (PIC), e.g., chloroaromatic compounds, can be used to characterise the emissions from combustion processes, like municipal or hazardous waste incineration. A possible application of such relationships may be the on-line real-time monitoring of a characteristic surrogate, e.g., with Resonance-Enhanced Multiphoton Ionization-Time-of-Flight Mass Spectrometry (REMPI-TOFMS). In this paper, we report the relationships of homologues and individual congeners of chlorinated benzenes (PCBz), dibenzo-p-dioxins (PCDD), dibenzofurans (PCDF) and phenols (PCPh) to the International Toxicity Equivalent (I-TEQ) of the PCDD/F (I-TEQ value) in the flue gas and stack gas of a 22 MW hazardous waste incinerator (HWI). As the REMPI detection sensitivity is decreasing with the increase of the degree of chlorination, this study focuses on the lower chlorinated species of the compounds mentioned above. Lower chlorinated species, e.g., chlorobenzene (MCBz), 1,4-dichlorobenzene, 2,4,6-trichlorodibenzofuran or 2,4-dichlorophenol, were identified as I-TEQ surrogates in the flue gas. In contrast to the higher chlorinated phenols, the lower chlorinated phenols (degree of chlorination 4) were not reliable as surrogates in the stack gas. The identified surrogates are evaluated in terms of their detectability by REMPI-TOFMS laser mass spectrometry. The outcome is that MCBz is the best suited surrogate for (indirect) on-line measuring of the I-TEQ value in the flue gas by REMPI-TOFMS. The correlation coefficient r of the MCBz concentration to the I-TEQ in the flue gas was 0.85.

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