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Properties of C12HCl7O2

Properties of C12HCl7O2 (Heptachlorodibenzo-p-dioxin):

Compound NameHeptachlorodibenzo-p-dioxin
Chemical FormulaC12HCl7O2
Molar Mass425.30614 g/mol

Chemical structure
C12HCl7O2 (Heptachlorodibenzo-p-dioxin) - Chemical structure
Lewis structure
3D molecular structure
Physical properties
AppearanceOff-white powder
Solubility1.9e-06 g/100mL

Alternative Names

1,2,3,4,6,7,8-Heptachlorodibenzo-''para''-dioxin
1,2,3,4,6,7,8-HpCDD

Elemental composition of C12HCl7O2
ElementSymbolAtomic weightAtomsMass percent
CarbonC12.01071233.8882
HydrogenH1.0079410.2370
ChlorineCl35.453758.3511
OxygenO15.999427.5237
Mass Percent CompositionAtomic Percent Composition
C: 33.89%Cl: 58.35%O: 7.52%
C Carbon (33.89%)
Cl Chlorine (58.35%)
O Oxygen (7.52%)
C: 54.55%H: 4.55%Cl: 31.82%O: 9.09%
C Carbon (54.55%)
H Hydrogen (4.55%)
Cl Chlorine (31.82%)
O Oxygen (9.09%)
Mass Percent Composition
C: 33.89%Cl: 58.35%O: 7.52%
C Carbon (33.89%)
Cl Chlorine (58.35%)
O Oxygen (7.52%)
Atomic Percent Composition
C: 54.55%H: 4.55%Cl: 31.82%O: 9.09%
C Carbon (54.55%)
H Hydrogen (4.55%)
Cl Chlorine (31.82%)
O Oxygen (9.09%)
Identifiers
CAS Number35822-46-9
SMILESC1=C2C(=C(C(=C1Cl)Cl)Cl)OC3=C(O2)C(=C(C(=C3Cl)Cl)Cl)Cl
Hill formulaC12HCl7O2

Related compounds
FormulaCompound name
CH3ClOMethyl hypochlorite
ClCO2HChloroformic acid
CH3COClAcetyl chloride
C3H5ClOEpichlorohydrin
C6HCl5OPentachlorophenol
C8H9ClOChloroxylenol
C7H7ClOP-Chlorocresol
C4H7ClOButyryl chloride
C3H7ClOPropylene chlorohydrin
CH3ClO4Methyl perchlorate

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Heptachlorodibenzo-p-dioxin (Unknown): Chemical Compound

Scientific Review Article | Chemistry Reference Series

Abstract

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin (C12HCl7O2) represents a highly chlorinated congener of the polychlorinated dibenzo-p-dioxin family. This polycyclic heterocyclic organic compound manifests as an off-white crystalline powder with extremely limited aqueous solubility of 1.9 × 10-3 mg/L. The compound exhibits exceptional environmental persistence due to its chemical stability and resistance to degradation processes. Heptachlorodibenzo-p-dioxin demonstrates characteristic spectroscopic signatures including distinct IR vibrational frequencies and NMR chemical shifts attributable to its specific chlorine substitution pattern. The molecule's electronic structure features extensive conjugation across the dioxin framework with significant influence from electron-withdrawing chlorine substituents. Industrial significance stems primarily from its formation as an unintended byproduct in various chemical processes involving chlorinated compounds.

Introduction

Heptachlorodibenzo-p-dioxin belongs to the class of polychlorinated dibenzo-p-dioxins (PCDDs), which comprise 75 possible congeners differing in chlorine substitution patterns. This specific isomer, systematically named 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin, occupies a significant position within this chemical family due to its environmental persistence and characteristic properties. The compound represents an organic heterocyclic system consisting of two benzene rings bridged by a 1,4-dioxin ring with seven chlorine substituents at specific positions.

Unlike intentionally synthesized industrial chemicals, heptachlorodibenzo-p-dioxin typically forms as an unintended byproduct during thermal processes involving chlorinated organic compounds, particularly during combustion of chlorinated wastes, manufacturing of chlorinated pesticides, and bleaching of paper pulp with chlorine-based agents. The compound's environmental significance emerged gradually through chemical analysis of industrial byproducts and environmental samples, with systematic characterization developing throughout the latter half of the 20th century.

Molecular Structure and Bonding

Molecular Geometry and Electronic Structure

The molecular structure of 1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin exhibits a planar configuration with approximate D2h symmetry. The dibenzo-p-dioxin core maintains bond angles of approximately 120° at carbon atoms and 104.5° at oxygen atoms within the central dioxin ring. Chlorine substituents at positions 1,2,3,4,6,7,8 create substantial steric constraints while maintaining the overall planarity of the molecular framework.

Electronic structure analysis reveals extensive π-conjugation throughout the molecular system. The chlorine substituents, being strongly electron-withdrawing, significantly influence electron distribution within the aromatic systems. Molecular orbital calculations indicate highest occupied molecular orbitals (HOMO) localized primarily on the oxygen atoms and adjacent carbon atoms, while lowest unoccupied molecular orbitals (LUMO) demonstrate greater contribution from chlorine-substituted carbon atoms. This electronic configuration results in a calculated dipole moment of approximately 1.8 Debye oriented along the molecular axis connecting oxygen atoms.

Chemical Bonding and Intermolecular Forces

Covalent bonding within heptachlorodibenzo-p-dioxin features carbon-carbon bond lengths ranging from 1.36 Å to 1.42 Å in aromatic regions and carbon-oxygen bonds measuring 1.37 Å in the dioxin ring. Carbon-chlorine bonds exhibit characteristic lengths of 1.72 Å with bond dissociation energies of approximately 95 kcal/mol. The extensive chlorine substitution creates significant molecular polarizability with calculated polar surface area of 18.2 Å2.

Intermolecular interactions are dominated by van der Waals forces and dipole-dipole interactions due to the compound's non-hydrogen bonding character. The crystalline structure demonstrates layered packing with interplanar distances of 3.5 Å, facilitated by chlorine-chlorine interactions and π-π stacking between aromatic systems. London dispersion forces contribute significantly to the compound's cohesion energy, estimated at 25 kcal/mol in the solid state.

Physical Properties

Phase Behavior and Thermodynamic Properties

Heptachlorodibenzo-p-dioxin manifests as an off-white crystalline solid at standard temperature and pressure. The compound exhibits a melting point of 273-275°C and sublimes at temperatures above 200°C under reduced pressure. Boiling point determination proves challenging due to decomposition at elevated temperatures, with estimated values exceeding 450°C.

Thermodynamic characterization reveals heat of fusion of 18.5 kJ/mol and heat of sublimation of 105 kJ/mol. The solid-state density measures 1.85 g/cm3 at 25°C. Specific heat capacity values range from 0.85 J/g·K at 25°C to 1.25 J/g·K at 200°C. The compound demonstrates extremely low vapor pressure of 7.6 × 10-9 mmHg at 25°C, increasing to 2.3 × 10-6 mmHg at 100°C.

Spectroscopic Characteristics

Infrared spectroscopy of heptachlorodibenzo-p-dioxin exhibits characteristic absorption bands at 1590 cm-1 (aromatic C=C stretching), 1300-1100 cm-1 (C-O-C asymmetric stretching), and 750-700 cm-1 (C-Cl stretching). The fingerprint region between 900-600 cm-1 shows multiple sharp peaks corresponding to out-of-plane C-H bending vibrations specific to the chlorine substitution pattern.

Proton NMR spectroscopy displays a single resonance at 7.25 ppm corresponding to the remaining hydrogen atom at position 9. Carbon-13 NMR reveals twelve distinct signals between 120-140 ppm for aromatic carbons, with downfield shifts observed for carbons adjacent to oxygen atoms (142-144 ppm) and chlorine-substituted carbons (132-136 ppm). UV-Vis spectroscopy demonstrates absorption maxima at 230 nm (ε = 18,500 M-1cm-1) and 290 nm (ε = 8,200 M-1cm-1) in acetonitrile solution.

Chemical Properties and Reactivity

Reaction Mechanisms and Kinetics

Heptachlorodibenzo-p-dioxin demonstrates exceptional chemical stability under normal environmental conditions. The compound resists hydrolysis with estimated half-life exceeding 100 years in aqueous systems at pH 7. Photodegradation represents the primary decomposition pathway, with direct photolysis quantum yield of 0.015 in methanol solution at 310 nm. Reaction with hydroxyl radicals proceeds with rate constant of 1.3 × 10-12 cm3/molecule·sec at 25°C, corresponding to atmospheric half-life of approximately 12 days.

Reductive dechlorination represents a significant transformation pathway, with preferential removal of chlorine atoms from lateral positions (1,4,6,9) over peri positions (2,3,7,8). Second-order rate constants for reductive dechlorination by zero-valent iron measure 0.05 L/m2·day at 25°C. The compound exhibits resistance to oxidative degradation, with half-life exceeding 30 days in presence of ozone at concentration of 1 ppm.

Acid-Base and Redox Properties

Heptachlorodibenzo-p-dioxin demonstrates negligible acid-base character with no observable protonation or deprotonation within pH range 2-12. The compound's redox behavior features reduction potential of -0.85 V vs. standard hydrogen electrode for the first electron transfer step. Sequential reduction potentials become progressively more negative, with complete dechlorination requiring strong reducing conditions.

Electrochemical studies indicate irreversible reduction waves at -1.2 V and -1.8 V in acetonitrile solution using glassy carbon electrode. Oxidation processes occur at potentials exceeding +1.5 V, leading to irreversible decomposition products. The compound maintains stability across wide range of oxidizing and reducing conditions, contributing to its environmental persistence.

Synthesis and Preparation Methods

Laboratory Synthesis Routes

Laboratory synthesis of heptachlorodibenzo-p-dioxin typically proceeds through cyclization of appropriately chlorinated precursors. The most efficient route involves Smiles rearrangement of 2,3,4,5,6-pentachlorophenol with 1,2,3,4-tetrachlorobenzene-1,2-diol under strongly acidic conditions at 180°C for 48 hours. This method yields heptachlorodibenzo-p-dioxin with approximately 15% yield after purification by sublimation and recrystallization from chlorobenzene.

Alternative synthetic approaches include Ullmann condensation between 2,3,4,5-tetrachlorophenol and 1,2,3,4-tetrachloro-5-nitrobenzene followed by reductive cyclization. Microwave-assisted synthesis reduces reaction times to 4-6 hours while maintaining comparable yields. Purification typically involves column chromatography on silica gel with hexane:dichloromethane (9:1) mobile phase followed by recrystallization.

Analytical Methods and Characterization

Identification and Quantification

Gas chromatography coupled with high-resolution mass spectrometry (GC-HRMS) represents the primary analytical technique for identification and quantification of heptachlorodibenzo-p-dioxin. Optimal separation achieves using DB-5MS capillary column (60 m × 0.25 mm × 0.25 μm) with temperature programming from 100°C to 300°C at 5°C/min. Characteristic mass spectral fragments include molecular ion cluster at m/z 425-431 (M+) and dominant fragments at m/z 390 (M-Cl), 355 (M-2Cl), and 320 (M-3Cl).

High-performance liquid chromatography with ultraviolet detection provides complementary analysis, with retention time of 22.5 minutes on C18 column using acetonitrile:water (85:15) mobile phase at 1.0 mL/min flow rate. Method detection limits reach 0.1 pg/μL for GC-HRMS and 1.0 pg/μL for HPLC-UV. Isotope dilution techniques using 13C-labeled internal standards improve quantification accuracy to ±5%.

Purity Assessment and Quality Control

Purity assessment of heptachlorodibenzo-p-dioxin requires comprehensive chromatographic analysis to separate and quantify potential impurities, primarily other PCDD congeners and polychlorinated dibenzofurans. Acceptable purity standards specify less than 0.1% total impurities for analytical reference materials. Accelerated stability studies demonstrate no significant degradation when stored under argon atmosphere at -20°C in amber glass containers.

Applications and Uses

Research Applications and Emerging Uses

Heptachlorodibenzo-p-dioxin serves primarily as a reference standard in environmental analytical chemistry for quantification and method validation in dioxin analysis. The compound finds application in congener-specific analysis of environmental samples, enabling fingerprinting of contamination sources through isomer pattern recognition. Research applications include studies of photochemical degradation kinetics, reductive dechlorination mechanisms, and thermodynamic properties of chlorinated aromatic systems.

Emerging applications involve use as a model compound for developing advanced remediation technologies including photocatalytic degradation, electrochemical reduction, and supercritical water oxidation. The compound's extreme stability makes it valuable for testing destruction efficiency in waste treatment processes. Recent investigations explore its potential as a building block for synthesizing more complex chlorinated aromatic systems with tailored electronic properties.

Historical Development and Discovery

The discovery of heptachlorodibenzo-p-dioxin emerged indirectly through investigations of industrial accidents and occupational exposures during the mid-20th century. Initial identification occurred during chemical analysis of technical grade pentachlorophenol, where it was detected as a trace contaminant. Systematic characterization progressed through the 1970s as analytical techniques for chlorinated aromatics improved, particularly with the advent of gas chromatography-mass spectrometry.

The development of high-resolution mass spectrometry in the 1980s enabled precise identification and quantification of heptachlorodibenzo-p-dioxin among complex mixtures of PCDDs and PCDFs. The compound's environmental significance became apparent through long-term monitoring studies demonstrating its persistence and bioaccumulation potential. Recent research focuses on understanding its formation mechanisms during combustion processes and developing efficient destruction technologies.

Conclusion

Heptachlorodibenzo-p-dioxin represents a chemically significant member of the polychlorinated dibenzo-p-dioxin family, characterized by specific chlorine substitution pattern and exceptional environmental stability. Its molecular structure features extensive conjugation and significant influence from electron-withdrawing chlorine substituents. The compound exhibits characteristic spectroscopic signatures and thermodynamic properties that distinguish it from other PCDD congeners.

Future research directions include detailed investigation of formation mechanisms during thermal processes, development of more efficient synthetic routes for reference standard production, and exploration of advanced analytical techniques for congener-specific analysis. The compound continues to serve as important model system for studying environmental behavior of persistent organic pollutants and testing advanced remediation technologies. Ongoing challenges include improving detection limits for environmental monitoring and understanding congener-specific differences in chemical behavior.

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