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1,3,4,7,9-PENTACHLORODIBENZOFURAN is a chlorinated organic compound that belongs to the family of dibenzofuran compounds. It is characterized by the presence of five chlorine atoms at the 1, 3, 4, 7, and 9 positions, which gives it unique chemical and physical properties. Due to its structural similarity to dioxins, it has been widely studied and used as a reference compound in various applications.

70648-20-3

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70648-20-3 Usage

Uses

Used in Environmental Testing and Research:
1,3,4,7,9-PENTACHLORODIBENZOFURAN is used as a standard in environmental testing and research for the analysis and monitoring of dioxin-like compounds. Its use as a reference compound helps in the accurate identification and quantification of these toxic substances in environmental samples, such as soil, water, and air.
Used in Measurement of Dioxins:
1,3,4,7,9-PENTACHLORODIBENZOFURAN is also used in the measurement of dioxins, which are a group of highly toxic and persistent environmental pollutants. These dioxins can be formed as by-products during various industrial processes, such as the production of pesticides and the incineration of waste. The use of 1,3,4,7,9-PENTACHLORODIBENZOFURAN as a standard allows for the accurate determination of dioxin levels in various samples, enabling the assessment of potential health risks and the implementation of appropriate control measures.
Used in Exposure Assessment of Pesticides to UV Light:
1,3,4,7,9-PENTACHLORODIBENZOFURAN is utilized in the study of the exposure of pesticides to ultraviolet (UV) light. When pesticides containing chlorinated compounds are exposed to UV light, they can undergo photochemical reactions, leading to the formation of dioxin-like compounds. The use of 1,3,4,7,9-PENTACHLORODIBENZOFURAN as a reference compound helps in understanding the formation and release of these toxic substances into the environment, which is crucial for the development of safer and more sustainable pesticide formulations.

Check Digit Verification of cas no

The CAS Registry Mumber 70648-20-3 includes 8 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 5 digits, 7,0,6,4 and 8 respectively; the second part has 2 digits, 2 and 0 respectively.
Calculate Digit Verification of CAS Registry Number 70648-20:
(7*7)+(6*0)+(5*6)+(4*4)+(3*8)+(2*2)+(1*0)=123
123 % 10 = 3
So 70648-20-3 is a valid CAS Registry Number.
InChI:InChI=1/C12H3Cl5O/c13-4-1-5(14)9-8(2-4)18-12-10(9)6(15)3-7(16)11(12)17/h1-3H

70648-20-3SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 16, 2017

Revision Date: Aug 16, 2017

1.Identification

1.1 GHS Product identifier

Product name 1,3,4,7,9-pentachlorodibenzofuran

1.2 Other means of identification

Product number -
Other names Dibenzofuran,1,3,4,7,9-pentachloro

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:70648-20-3 SDS

70648-20-3Downstream Products

70648-20-3Relevant academic research and scientific papers

Role of copper chloride in the formation of polychlorinated dibenzo-p-dioxins and dibenzofurans during incineration

Hatanaka, Takeshi,Kitajima, Akio,Takeuchi, Masao

, p. 73 - 79 (2007/10/03)

Combustion experiments in a laboratory-scale fluidized-bed reactor were performed to elucidate the role of copper chloride in formation of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) during model waste incineration. The amounts of PCDDs and PCDFs formed, the homologue profiles, and the isomer distributions were measured in the flue gas from incineration of model wastes containing various levels of copper. A correlation was found between the Cu content of the waste and the proportion of each congener. An increase in copper enhanced the formation of certain congeners, showing that copper acts as a catalyst for formation of PCDDs and PCDFs. An increase in the copper content of the waste decreased the CO concentration in the flue gas and reduced the formation of PCDDs and PCDFs during incineration. This indicates that copper also works as an oxidation catalyst to promote combustion, leading to lower concentrations of products of incomplete combustion. It is indispensable to consider both roles of the catalyst, i.e., enhancement and suppression, in the formation of PCDDs and PCDFs during waste incineration, which are estimated separately from the isomer distributions and the amounts of PCDDs and PCDFs formed.

De novo synthesis mechanism of polychlorinated dibenzofurans from polycyclic aromatic hydrocarbons and the characteristic isomers of polychlorinated naphthalenes

Iino,Imagawa,Takeuchi,Sadakata

, p. 1038 - 1043 (2007/10/03)

Polychlorinated dibenzofurans (PCDFs) and polychlorinated naphthalenes (PCNs) are known to be emitted from municipal waste incinerators (MWIs) with polychlorinated dibenzo-p-dioxins (PCDDs). Two formation paths for PCDD/Fs could mainly work, which are condensation of the precursors such as chlorophenols and 'de novo' formation from carbon. However the correlation between the chemical structure of carbon and the resulting PCDD/Fs still remains unknown. In this study, the PCDD/Fs formation from polycyclic aromatic hydrocarbons (PAHs) and CuCl was examined at 400 under 10% O2. Coronene among the PAHs characteristically gave 1,2,8,9-T4CDF and the derivatives. These isomers clearly indicate that chlorination causes the cleavage of the C-C bonds in a coronene molecule and also that oxygen is easily incorporated from its outside to form 1,2,8,9-T4CDF. The symmetrical preformed structures in the coronene molecule enabled to amplify the de novo formation of the isomer. PCNs are also formed directly from these PAHs. Since there have been few reports on the formation mechanism of PCNs, this study will be a first step to know the whole formation paths. We also define the de novo synthesis as the breakdown reaction of a carbon matrix, since the word has been used without the precise definition.

Isomer distributions of polychlorinated dibenzo-p-dioxins/dibenzofurans formed during de novo synthesis on incinerator fly ash

Addink, Ruud,Govers, Harrie A. J.,Olie, Kees

, p. 1888 - 1893 (2007/10/03)

Polychlorinated dibenzo-p-dioxins (PCDD) and dibenzofurans (PCDF) emitted from municipal waste incinerators appear to have a chlorination pattern that is quite constant across various samples and conditions. This suggested that these patterns may be controlled by thermodynamic properties of the individual PCDD/F congeners, such as the free Gibbs energy of formation (Δg°(f,T)). This would make prediction of the isomer composition of a particular sample (and hence its TEQ value) possible, based on values of ΔG°(f,T). A laboratory scale study was carried out with activated carbon on fly ash as the source of PCDD/F formation. Although it was found that the isomer distributions within homologues were independent of the reaction time (proof of thermodynamic control), other observations (lack of equilibrium/isomerization between isomers and lack of similarity between isomer distributions measured and predicted by ΔG°(f,T)) contradicted the possibility of thermodynamic control. Hence, this study could not confirm that de novo formation of PCDD/F could explain thermodynamically controlled isomer distributions in incinerators. Some recommendations for further work- time-based studies with precursors, isomerization studies with single congeners, and more data on ΔG°(f,T) values of PCDD/F-were made. Polychlorinated dibenzo-p-dioxins (PCDD) and dibenzofurans (PCDF) emitted from municipal waste incinerators appear to have a chlorination pattern that is quite constant across various samples and conditions. This suggested that these patterns may be controlled by thermodynamic properties of the individual PCDD/F congeners, such as the free Gibbs energy of formation (ΔG°f,T). This would make prediction of the isomer composition of a particular sample (and hence its TEQ value) possible, based on values of ΔG°f,T. A laboratory scale study was carried out with activated carbon on fly ash as the source of PCDD/F formation. Although it was found that the isomer distributions within homologues were independent of the reaction time (proof of thermodynamic control), other observations (lack of equilibrium/isomerization between isomers and lack of similarity between isomer distributions measured and predicted by ΔG°f,T) contradicted the possibility of thermodynamic control. Hence, this study could not confirm that de novo formation of PCDD/F could explain thermodynamically controlled isomer distributions in incinerators. Some recommendations for further work - time-based studies with precursors, isomerization studies with single congeners, and more data on ΔG°f,T values of PCDD/F - were made.

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