JUN 8, 202670 MINS READ
The direct chlorination of ethylene represents the most straightforward synthetic pathway to ethylene dichloride, involving the exothermic addition of molecular chlorine across the ethylene double bond in liquid-phase reaction systems. This process operates under carefully controlled conditions to maximize EDC selectivity while suppressing undesirable side reactions that generate chlorinated by-products 1. The reaction proceeds via a radical mechanism initiated by trace iron species or deliberately added catalysts, with the overall stoichiometry represented as: C₂H₄ + Cl₂ → ClCH₂CH₂Cl (ΔH ≈ -218 kJ/mol) 4.
Industrial direct chlorination processes utilize ethylene dichloride itself as the reaction solvent, creating a homogeneous liquid-phase environment that facilitates heat removal and product separation 13. The circulating EDC medium is maintained below its vaporization point (approximately 83.5°C at atmospheric pressure) to ensure liquid-phase operation, with reaction temperatures typically controlled between 100-125°C under moderate pressure 3. Patent literature demonstrates that EDC solvent purity significantly impacts by-product formation rates: maintaining solvent purity between 85-99.8% (preferably 90-99.8%) effectively suppresses the generation of trichloroethane, chloral, and other chlorinated contaminants 3. The reaction zone design incorporates external heat exchangers connected via thermosyphon circulation loops, where the exothermic heat of reaction drives continuous medium flow through indirect cooling systems 4. This configuration enables precise temperature control while preventing localized hot spots that would otherwise promote side reactions leading to carbon tetrachloride (CCl₄), chloroform (CHCl₃), and 1,1,2-trichloroethane formation 316.
Optimal EDC selectivity requires careful control of the ethylene-to-chlorine molar ratio, with industrial practice favoring slight ethylene excess to ensure complete chlorine consumption 3. Research data indicates that maintaining ethylene/chlorine ratios between 1.0-1.2 (preferably 1.05-1.15) minimizes residual chlorine in the product stream while avoiding excessive ethylene losses to vent streams 3. Operating at the lower end of this range (1.0-1.05) increases the risk of unreacted chlorine carryover, which can initiate secondary chlorination reactions producing polychlorinated by-products 3. Conversely, excessive ethylene ratios (>1.2) reduce per-pass conversion efficiency and necessitate larger recycle streams, increasing compression costs and energy consumption 3. Temperature control within the 110-120°C range provides the optimal balance between reaction kinetics and selectivity, with higher temperatures (>125°C) accelerating undesirable thermal decomposition pathways 3.
While direct chlorination proceeds via a radical mechanism that can occur without added catalysts, industrial processes often employ iron-containing reaction vessels or deliberately introduce iron compounds to enhance reaction rates 8. The catalytic effect of iron species (Fe²⁺/Fe³⁺) involves the formation of iron-chlorine complexes that facilitate homolytic Cl-Cl bond cleavage, generating chlorine radicals that initiate the chain propagation sequence 8. Patent disclosures describe reaction systems utilizing iron tubes or iron-lined reactors operating at 150 psig (approximately 10.3 bar gauge pressure) with chlorine introduced through multiple injection nozzles to maintain uniform concentration profiles 8. Alternative catalytic approaches include selenium tetrachloride (SeCl₄) and phosphorus pentachloride (PCl₅) systems, which demonstrate enhanced selectivity under specific conditions 5. The SeCl₄/PCl₅ catalyst combination operates effectively in EDC solvent with oxygen concentrations controlled between 0.06-1.0 vol% (preferably 0.6-1.0 vol%), achieving superior yields compared to uncatalyzed systems 5.
Oxychlorination represents the second major industrial route for EDC synthesis, converting ethylene, hydrogen chloride, and oxygen (or air) into ethylene dichloride and water over heterogeneous catalysts 18. This process plays a crucial role in integrated VCM production facilities by recycling the HCl generated during EDC thermal cracking back into the production cycle, thereby achieving near-complete chlorine utilization 1314. The overall reaction stoichiometry is: C₂H₄ + 2HCl + ½O₂ → ClCH₂CH₂Cl + H₂O (ΔH ≈ -238 kJ/mol) 18.
Industrial oxychlorination predominantly employs fluidized bed reactor technology, which provides superior temperature control and catalyst management compared to fixed bed alternatives 18. Fluidized bed systems operate with finely divided catalyst particles (typically 40-150 μm diameter) suspended in the upward-flowing reactant gas stream, creating a turbulent, well-mixed reaction environment with minimal temperature gradients 18. This configuration enables continuous catalyst addition and withdrawal without process shutdown, facilitating catalyst activity maintenance and impurity management 18. Conventional oxychlorination processes operate at temperatures exceeding 220°C to ensure high HCl conversion (typically >98%) and minimize acid carryover to downstream equipment 18. However, elevated temperatures simultaneously promote undesirable side reactions that generate carbon monoxide, carbon dioxide, and chlorinated hydrocarbon by-products including ethyl chloride, 1,1,2-trichloroethane, chloral, chloroform, and carbon tetrachloride 18. Recent process innovations demonstrate that pre-heating fluidizable catalysts to temperatures above 150°C for extended periods (>6 hours) under fluidization conditions prior to ethylene introduction significantly improves subsequent EDC selectivity and reduces by-product formation rates 18.
Oxychlorination catalysts typically comprise copper chloride (CuCl₂) as the active component supported on high-surface-area carriers such as alumina, silica, or zeolites 6. The copper species undergo redox cycling between Cu²⁺ and Cu⁺ oxidation states during the catalytic cycle, with the Cu²⁺ form activating HCl and ethylene while the Cu⁺ form reacts with oxygen to regenerate the active Cu²⁺ species 6. Alkali metal chlorides (particularly KCl) are frequently incorporated as promoters to enhance catalyst stability and selectivity 18. Zeolite-supported catalysts demonstrate particular utility in selective oxyhalogenation reactions, enabling conversion of ethyl chloride (a common by-product) back to EDC and ethylene at temperatures between 180-350°C 6. This catalytic approach provides an effective strategy for managing by-product streams in integrated production facilities 6.
Industrial oxychlorination processes invariably operate with excess ethylene relative to stoichiometric requirements to ensure complete HCl conversion and prevent acid breakthrough to product streams 18. Typical ethylene excess ranges from 5-15 mol% above stoichiometric, with the unreacted ethylene recovered from reactor off-gas and recycled to the process 11. The recovered ethylene stream requires drying before recycle to prevent water accumulation in the reactor feed; this drying step is efficiently accomplished by contact with liquid EDC, which absorbs water while allowing ethylene to pass through 11. The dried ethylene can then be reacted with chlorine in a liquid-phase direct chlorination unit to recover additional EDC, effectively integrating the two primary synthesis routes 11. This integrated approach minimizes ethylene losses and reduces the air pollution potential associated with ethylene venting 11.
Both direct chlorination and oxychlorination routes generate complex product mixtures containing EDC as the major component along with various chlorinated hydrocarbon by-products, unreacted reactants, and inorganic impurities 21016. Effective purification strategies are essential to produce polymer-grade EDC suitable for VCM production, as impurities can poison downstream cracking catalysts, promote coke formation, and degrade final PVC product quality 1014.
The primary lower-boiling impurities in crude EDC streams include ethyl chloride (b.p. 12.3°C), vinyl chloride (b.p. -13.8°C), chloroform (b.p. 61.2°C), and carbon tetrachloride (b.p. 76.7°C) 16. Conventional purification schemes employ light ends distillation columns operating under reflux conditions to separate these components as overhead fractions 1415. Patent literature describes specialized reflux control strategies for chloroform/carbon tetrachloride separation, maintaining chloroform concentrations greater than 51.5 mole percent in the reflux liquid to minimize EDC losses to the light fraction 16. This approach exploits the azeotropic behavior of the EDC-chloroform-carbon tetrachloride ternary system to achieve efficient separation with reduced energy consumption 16.
Higher-boiling impurities in crude EDC include 1,1,2-trichloroethane (b.p. 113.8°C), trichloroethylene (b.p. 87.2°C), benzene (b.p. 80.1°C), and various chlorinated aromatics 10. Heavy ends distillation columns separate these components as bottom streams, producing high-purity EDC overhead product (typically >99.5% purity) 1415. Extractive distillation techniques employing high-boiling chloroalkene solvents such as perchloroethylene (tetrachloroethylene, b.p. 121.1°C) enable selective removal of unsaturated impurities including trichloroethylene and benzene, which are particularly problematic due to their tendency to polymerize and form coke deposits in downstream thermal cracking furnaces 10. The extractive distillation process operates by preferentially dissolving the unsaturated impurities in the perchloroethylene solvent phase, allowing purified EDC to be recovered as a separate phase 10.
Modern EDC purification processes incorporate waste heat recovery systems that utilize thermal energy from the exothermic chlorination/oxychlorination reactions or from downstream VCM pyrolysis operations to drive distillation column reboilers 1419. This integration significantly reduces the external energy requirements for purification and improves overall process economics 1419. Patent disclosures describe configurations where the EDC feed to heavy ends distillation columns is preheated using waste heat from the EDC manufacturing process itself, the subsequent EDC pyrolysis step, or the oxychlorination unit 1419. Additional purification steps include washing with substantially anhydrous monoethylene glycol to remove residual water, acids, and polar impurities such as 2-chloroethanol 7. Phase separation systems exploit the limited mutual solubility of EDC and aqueous phases to decant the heavier EDC-rich phase from water-containing streams, with the aqueous phase containing residual reactants and by-products recycled to upstream process units 7.
Beyond the conventional direct chlorination and oxychlorination pathways, several alternative synthetic routes to ethylene dichloride have been developed to address specific feedstock availability scenarios or to enable production from renewable resources 713.
A recently disclosed process enables EDC production from monoethylene glycol (MEG) and hydrogen chloride, offering a potential pathway from bio-based or CO₂-derived ethylene glycol to chlorinated intermediates 7. The process involves reacting MEG with HCl in the presence of water under conditions that promote sequential conversion of MEG to 2-chloroethanol and subsequently to EDC 7. The reaction generates water as a by-product, which aids in separating residual reactants and polar by-products from the EDC-rich product phase 7. Key process innovations include operating under conditions that limit both 2-chloroethanol and EDC concentrations in the vapor phase, thereby facilitating high conversion efficiencies (approaching complete MEG conversion) while minimizing EDC losses 7. Phase separation systems decant the heavier EDC phase (density ≈ 1.25 g/cm³) from the aqueous phase (density ≈ 1.0 g/cm³), with the aqueous phase containing unconverted MEG and 2-chloroethanol recycled to the reactor 7. Additional purification via washing with substantially anhydrous MEG removes residual water, acids, and 2-chloroethanol, producing high-purity EDC (>99%) suitable for VCM production 7. This route addresses the challenge of producing EDC from sustainable resources, though commercial viability depends on MEG feedstock costs and HCl availability 7.
An alternative approach involves the direct conversion of ethane to EDC via autothermic (self-sustaining) cracking in the presence of chlorine and oxygen 13. Ethane is introduced into a high-temperature reaction zone (700-1000°C) together with controlled proportions of chlorine and oxygen, where it undergoes partial oxidation and chlorination to produce a mixture containing predominantly ethylene and hydrogen chloride 13. The reaction mixture is quenched with a volatile liquid and then passed to a catalytic oxyhydrochlorination zone where the ethylene, HCl, and oxygen are converted to EDC 13. This integrated process achieves 20-95% ethane conversion with 74-96% ethylene yield (based on converted ethane), with substantially complete utilization of the generated HCl 13. The process can be configured to produce EDC, VCM, or mixtures thereof depending on downstream processing options 13. While this route offers potential advantages in regions with abundant ethane availability (e.g., from natural gas liquids), the high-temperature cracking step requires specialized reactor materials and careful control to prevent excessive coke formation 13.
The primary industrial application of ethylene dichloride is as the intermediate for vinyl chloride monomer production, with over 95% of global EDC production directed to this end use 1415. Two principal conversion technologies are employed: thermal cracking (pyrolysis) and catalytic dehydrochlorination 917.
Thermal cracking of EDC to VCM proceeds via a radical mechanism at temperatures typically ranging from 480-530°C, with the overall reaction: ClCH₂CH₂Cl → CH₂=CHCl + HCl (ΔH ≈ +71 kJ/mol) 1415. The endothermic nature of the reaction necessitates continuous heat input, typically provided by fired heaters or molten salt heating systems 17. Industrial pyrolysis reactors operate at pressures between 15-30 bar to maintain liquid-phase conditions at the reactor inlet while allowing vapor-phase reaction in the high-temperature zone 17. Per-pass EDC conversion is deliberately limited to 50-65% to minimize secondary reactions that generate chlorinated by-products and coke deposits on reactor tube walls 17. The reactor effluent is quenched and subjected to distillation to separate VCM product, unreacted EDC (recycled to the pyrolysis reactor), and HCl (recycled to the oxychlorination unit) 1415. Coke formation on reactor tube internal surfaces represents a major operational challenge, necessitating periodic decoking operations that reduce plant availability 10. Innovations in pyrolysis technology include the integration of catalytic reactors downstream of the thermal cracking unit to convert residual EDC and intermediate species to VCM, thereby increasing overall conversion efficiency without requiring additional heat input 17.
| Org | Application Scenarios | Product/Project | Technical Outcomes |
|---|---|---|---|
| LG CHEM. LTD. | Large-scale ethylene dichloride manufacturing facilities requiring high selectivity and minimal chlorinated by-products such as trichloroethane and chloral. | EDC Production Process | Optimized reaction parameters (85-99.8% EDC solvent purity, ethylene/chlorine ratio 1.0-1.2, temperature 100-125°C) effectively suppress by-product formation and improve EDC selectivity in direct chlorination synthesis. |
| THE DOW CHEMICAL COMPANY | Integrated VCM/PVC production facilities requiring efficient handling of ethyl chloride by-products from oxychlorination reactions. | Oxychlorination Process | Zeolite-supported copper chloride catalysts enable selective conversion of ethyl chloride by-product back to EDC and ethylene at 180-350°C, improving overall process economics and by-product management. |
| OXY VINYLS LP | Industrial oxychlorination reactors operating at temperatures exceeding 220°C where minimizing CO, CO2, and chlorinated by-product formation is critical. | Fluidized Bed Oxychlorination | Pre-heating fluidizable catalysts above 150°C for over 6 hours before ethylene introduction significantly improves EDC selectivity and reduces chlorinated hydrocarbon by-products (trichloroethane, chloral, carbon tetrachloride). |
| SOLVAY SA | Integrated EDC-VCM-PVC production complexes requiring energy-efficient separation of lower-boiling impurities (ethyl chloride, vinyl chloride, chloroform) and higher-boiling contaminants (trichloroethane, benzene). | EDC Purification System | Integrated waste heat recovery from chlorination/oxychlorination reactions or VCM pyrolysis operations drives distillation column reboilers, significantly reducing external energy requirements for EDC purification to >99.5% purity. |
| PPG INDUSTRIES INC. | EDC purification systems feeding thermal pyrolysis units where unsaturated impurity removal is essential to prevent catalyst poisoning and coke deposition in VCM production. | Extractive Distillation Process | Perchloroethylene solvent-based extractive distillation selectively removes unsaturated impurities (trichloroethylene, benzene) that cause coke formation in downstream thermal cracking furnaces, producing polymer-grade EDC. |