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1,3,8-trichlorooxanthrene is a chemical compound belonging to the family of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), which are known for their toxic and persistent nature in the environment. This specific compound consists of a dibenzo-p-dioxin molecule with three chlorine atoms attached at the 1, 3, and 8 positions. Due to its structural similarity to the highly toxic 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 1,3,8-trichlorooxanthrene exhibits certain toxic properties, although it is less potent than TCDD. It is primarily formed as a byproduct of industrial processes involving chlorine, such as waste incineration and chemical manufacturing, and can pose risks to human health and the environment if not properly managed.

82306-61-4

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82306-61-4 Usage

Chemical class

Polycyclic aromatic hydrocarbons (PAHs)

Derivative

Xanthene with three chlorine atoms

Chlorine attachment positions

1, 3, and 8

Natural occurrence

Not found in nature

Synthesis

Primarily for research purposes

Toxicity

Known to be toxic

Carcinogenicity

Potentially carcinogenic

Health effects

Linked to adverse health effects

Handling

Requires caution and appropriate safety protocols

Disposal

Must be disposed of following proper guidelines

Check Digit Verification of cas no

The CAS Registry Mumber 82306-61-4 includes 8 digits separated into 3 groups by hyphens. The first part of the number,starting from the left, has 5 digits, 8,2,3,0 and 6 respectively; the second part has 2 digits, 6 and 1 respectively.
Calculate Digit Verification of CAS Registry Number 82306-61:
(7*8)+(6*2)+(5*3)+(4*0)+(3*6)+(2*6)+(1*1)=114
114 % 10 = 4
So 82306-61-4 is a valid CAS Registry Number.

82306-61-4SDS

SAFETY DATA SHEETS

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

Version: 1.0

Creation Date: Aug 19, 2017

Revision Date: Aug 19, 2017

1.Identification

1.1 GHS Product identifier

Product name 1,3,8-trichlorodibenzo-p-dioxin

1.2 Other means of identification

Product number -
Other names Dibenzo-p-dioxin,1,3,8-trichloro

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:82306-61-4 SDS

82306-61-4Upstream product

82306-61-4Downstream Products

82306-61-4Relevant academic research and scientific papers

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.

Influence of variation in combustion conditions on the primary formation of chlorinated organic micropollutants during municipal solid waste combustion

Wikstroem,Tysklind,Marklund

, p. 4263 - 4269 (2007/10/03)

The aim of this study was to investigate the influence of variation in combustion conditions on the primary formation of organic micropollutants (OMPs). The flue gas samples were taken at a relatively high flue gas temperature (650°C), to enable mechanistic studies on the high temperature formation (primary formation). Eleven experiments were performed in a laboratory scale fluidized bed reactor fed with an artificial municipal solid waste (MSW). The samples were analyzed for mono- to octachlorinated dibenzo- p-dioxins and dibenzofurans (CDDs/Fs), tri- to decachlorinated biphenyls (CBs), di- to hexachlorinated benzenes (CBzs), and di- to pentachlorinated phenols (CPhs). In addition to chlorinated OMPs, nonchlorinated dibenzo-p- dioxin (DD), dibenzofuran (DF), and biphenyl (BP) were analyzed. The experiments show that variations in the CE influence the degree of chlorination of the organic micropollutants. A correlation between low CE and formation of non- and low-chlorinated DMPs was seen and a distinct relationship of higher chlorinated homologues and efficient combustion condition. Thus, the DiCDFs and DiCBzs are formed during low combustion efficiency (CE), while the PeCDF and PeCBzs formation take place at higher CE. The distribution between primary and secondary air is important for the formation of higher CDD/Fs and CBzs. The primary formation of CDDs and CDFs is through different mechanisms. The CDDs are mainly formed by condensation of CPhs, while the CDFs are formed through a non- or a low-chlorinated precursor followed by further chlorination reactions.

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