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Ascent Petrochem Holdings Co., Limited

1,1,1,2-Tetrachloroethane

    • Product Name: 1,1,1,2-Tetrachloroethane
    • Factroy Site: Lingwu, Yinchuan, Ningxia, China
    • Price Inquiry: sales2@ascent-chem.com
    • Manufacturer: Ascent Petrochem Holdings Co., Limited
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    Specifications
    HS Code 310346
    Cas Number 630-20-6
    Molecular Formula C2H2Cl4
    Molecular Weight 167.85 g/mol
    Melting Point -68.1 °C
    Boiling Point 130.5 °C
    Density 1.588 g/mL at 20 °C
    Vapor Pressure 12 mmHg at 20 °C
    Solubility In Water 0.11 g/100 mL at 20 °C
    Appearance Colorless liquid
    Flash Point 46 °C (closed cup)

    As an accredited 1,1,1,2-Tetrachloroethane factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing Packaged in 200 L steel drums with UN-approved closures, featuring hazard labels for toxicity and environmental precautions.
    Container Loading (20′ FCL) Load 1,1,1,2‑Tetrachloroethane in UN-approved drums, stow upright, secure tightly, label as hazardous, and segregate from incompatible materials.
    Shipping 1,1,1,2‑Tetrachloroethane (UN 1702, Class 6.1, PG III) is a toxic, clear liquid. Ship in tightly sealed, corrosion-resistant containers. Avoid contact with foodstuffs. Keep away from heat and ignition sources. Label as toxic and environmentally hazardous. Segregate from strong oxidizers.
    Storage Store `1,1,1,2‑Tetrachloroethane` in a cool, dry, well-ventilated area away from heat, open flames, and direct sunlight. Use tightly sealed containers made of stainless steel or compatible plastics. Isolate from strong oxidizers, reactive metals, and moisture to prevent decomposition. Implement secondary containment and ensure proper labeling to manage spill hazards.
    Shelf Life Stable for several years if stored properly in a cool, dry, dark place. Decomposes slowly, forming corrosive acidic byproducts.
    Application of 1,1,1,2-Tetrachloroethane

    In the continuous vapour-phase fluorination of 1,1,1,2-tetrachloroethane with anhydrous hydrogen fluoride over a promoted chromium-based catalyst, precise control of the HF:organic molar ratio within 6:1 to 12:1 is fundamental. The reaction is conducted in a multi-tube fixed-bed reactor fabricated from Hastelloy C-276 to withstand the combined corrosion of HCl and HF at wall temperatures approaching 450 °C. The catalyst, typically a fluorinated chromia (Cr2O3·xHF) supported on high-purity alumina and promoted with 0.5–2.0 wt% Ni or Zn to moderate activity, undergoes a gradual loss of selectivity due to coke deposition and partial chlorination. Spent catalyst exhibits a surface area decline from 40–60 m²/g to below 15 m²/g, tracked by inline BET monitoring of side-stream samples every 200 operating hours. Regeneration is performed in situ via air-dilution oxidation at 570 ± 5 °C, a window narrowed by the risk of chromia sublimation above 590 °C. The primary product, 1,1,1,2-tetrafluoroethane (HFC‑134a), requires separation from co-produced HCl, unreacted HF, and under-fluorinated intermediates such as 2‑chloro‑1,1,1‑trifluoroethane (HCFC‑133a) through a train of high-pressure distillation columns operating at 12–16 bar. Overhead purity of 99.95 % HFC‑134a is verified by gas chromatography per ASTM D5632‑12, with a moisture specification of < 10 ppmv measured by chilled-mirror dew-point analyser in accordance with ISO 8573‑1:2010. This supply chain bifurcates into automotive air-conditioning compressors designed under ISO 17584:2005 and into pharmaceutical metered-dose inhaler propellant grades that demand < 1.0 µg/g non-volatile residue, tested via ISO 10993‑18 extraction protocols. The entire manufacturing operation falls under SEVESO III Directive 2012/18/EU due to inventories of liquefied toxic gases exceeding lower-tier thresholds, and the CMR classification (Carc. Cat. 2, Repr. Cat. 2) mandates leak-tight transfer systems verified by ISO 15848‑1 fugitive emission testing at 6‑month intervals.

    Vapour-Phase Cracking to Tetrachloroethylene

    Tetrachloroethylene (PCE) is generated by subjecting 1,1,1,2-tetrachloroethane to high-temperature pyrolysis in a tubular flow reactor at 550–650 °C with a residence time limited to 0.5–2.0 seconds. A single-pass conversion of 70–85 % is typical when a BaCl₂-impregnated activated carbon catalyst is employed at 1.5–3.0 bar back-pressure, the catalyst itself experiencing a gradual loss of surface chlorine that necessitates re-chlorination with Cl₂ injection at 0.5 vol% every 72 hours. The cracking effluent is quenched rapidly to < 100 °C in a titanium shell-and-tube exchanger to suppress back-reaction with liberated HCl. After caustic scrubbing and fractional distillation, the PCE fraction meets ASTM D4081‑16 for dry-cleaning grade, with a required acid acceptance of > 0.05 N and a copper-strip corrosion rating of 1a after 3 h at 100 °C. Any deviation in the preheater outlet temperature beyond ± 3 °C has been traced on production-scale units to coking-induced hot spots that elevate hexachlorobenzene formation above the 5 mg/kg limit specified in EU Ecolabel Commission Decision 2014/312/EU.

    What Inhibitor Chemistry Prevents Acid Build-Up in High-Boil Degreasing?

    A stabilizer package comprising alkyl nitriles and epoxides is required to maintain solvent integrity when 1,1,1,2-tetrachloroethane is used in closed-loop vapour degreasers for heavy-duty engine parts and aluminium die-cast components. The boiling point of 130.5 °C allows removal of baked-on carbonized soils that lighter chlorinated solvents cannot soften, yet the elevated sump temperature accelerates radical-induced oxidation to phosgene, trichloroacetyl chloride, and HCl. Field experience with 0.8–1.5 wt% stabiliser blends—typically 4:1 nitromethane to 1,4-dioxane—has demonstrated that the water-displacement and acid-acceptance reserve, measured by ASTM D2942‑16, must be maintained above 0.10 wt% NaOH equivalent. When the reserve drops below this threshold, chloride-induced stress corrosion cracking of Type 316L stainless steel heating elements accelerates, with pit depths reaching 0.2 mm within 200 operating hours as documented in borescope inspections. Occupational exposure is stringently controlled under REACH Annex XVII Entry 30 and Directive 2004/37/EC: the 8‑hour TWA inhalation limit is 1 ppm (7 mg/m³) per EU OEL 2019/1831, verified by pumped thermal desorption tubes analysed via ISO 16017‑1:2000. Any open-top degreaser configuration is prohibited; only fully enclosed equipment with a refrigerated condensation zone and interlocked safety covers meeting EN 16282‑8:2017 is permitted in EU member states.

    Extraction of heat-sensitive oils and waxes from botanical matrices can utilise 1,1,1,2-tetrachloroethane as a non-polar process solvent, provided the equipment is sealed to prevent vapour loss, as the boiling point of 130.5 °C permits rapid solvent recovery under moderate vacuum. Applied solely in research and pilot-scale facilities compliant with ISO 10993‑5 for biocompatibility of extractables, this niche function requires prior authorisation under local CMR workplace regulations and is typically limited to batches below 50 litres.

    When Dehydrochlorination Yields Polymer-Grade Vinylidene Chloride

    The base-catalysed dehydrochlorination of 1,1,1,2-tetrachloroethane with aqueous NaOH at 80–110 °C in a stirred-tank reactor lined with PFA fluoropolymer yields 1,1-dichloroethylene (vinylidene chloride, VDC) at 90–95 % selectivity. A continuous-wash decantation system removes the organic phase before alkali concentration falls below 8 wt% to avoid side-reaction to sodium acetate if ethanol is present as co-solvent. The crude VDC monomer is stabilised with 200–400 ppm p-methoxyphenol (MEHQ) to prevent autopolymerisation during rectification; the overheads after distillation at 31.7 °C must exhibit a purity of 99.9 % by capillary GC per ASTM D3527‑15 with inhibitor content confirmed by UV spectrophotometry at 320 nm. This monomer is immediately copolymerised with vinyl chloride to produce PVDC barrier films for food packaging. The conversion step triggers EU Framework Regulation (EC) 1935/2004 on food-contact materials, and the final film must pass overall migration testing under EU 10/2011 simulant D (olive oil) at 40 °C for 10 days. A documented failure mode at > 1 % moisture in the NaOH feed is elevated dichloroacetylene formation beyond the 50 ppm safety threshold, a reactive hazard that has necessitated redundant explosion suppression systems on full-scale lines rated to NFPA 69:2019.

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    Certification & Compliance
    More Introduction

    1,1,1,2‑Tetrachloroethane (CAS 630‑20‑6), a colourless, non‑flammable liquid with molecular formula C₂H₂Cl₄ and molecular weight 167.85 g mol⁻¹, is supplied as technical‑grade product of purity ≥ 98.5 % (GC area%, ASTM D6806). Typical isomer impurities comprise 1,1,2,2‑tetrachloroethane at < 0.8 % and trichloroethylene at < 0.3 %; water content is held below 100 mg kg⁻¹ (ASTM D1533, refrigerated sample). The compound boils at 130.5 °C (101.3 kPa), exhibits a density of 1.54 g mL⁻¹ at 20 °C (ISO 758), and exerts a vapour pressure of 1.3 kPa at 20 °C. Unlike its lower‑chlorinated congener 1,1,1‑trichloroethane—phased out under the Montreal Protocol—1,1,1,2‑tetrachloroethane possesses zero ozone‑depletion potential but carries an elevated toxicity profile that mandates rigorous exposure controls. The comparative table below juxtaposes its physical properties with those of other industrial chlorinated solvents, illustrating the trade‑off between solvency and boiling point that defines its application niches.

    Property (Test Method)1,1,1,2‑Tetrachloroethane1,1,1‑TrichloroethaneTetrachloroethyleneTrichloroethyleneCarbon Tetrachloride
    Boiling point, °C (ASTM D1078)130.5 – 131.574.0 – 74.5121.287.276.8
    Density at 20 °C, g mL⁻¹ (ISO 758)1.540 – 1.5451.3371.6231.4641.594
    Vapour pressure at 20 °C, kPa1.313.31.97.812.1
    Kauri‑butanol value, mL (ASTM D1133)100 – 10512490130114
    Solubility in water, g (100 mL)⁻¹ at 25 °C0.050.070.0150.110.05
    Evaporation rate (n BuOAc = 1) (ASTM D3539)0.045.50.073.84.0

    How Does 1,1,1,2‑Tetrachloroethane’s Solvency Profile Compare with Other Chlorinated Solvents in Immersion Cleaning?

    In a standard open‑top vapour degreaser with a boil‑sump volume of 200 L, the elevated boiling point (130.5 °C) produces a dense vapour zone (vapour density > 6.0 relative to air) that achieves thorough condensation cleaning of intricate geometries, such as fuel‑injector nozzles with internal channels of 0.5 mm diameter. The Kauri‑butanol value of 100–105 (ASTM D1133) confers sufficient solvent power to dissolve heavy lithium‑based greases without resorting to the aggressiveness of trichloroethylene, thereby reducing the risk of environmental stress‑cracking in polycarbonate sight‑glasses. Because the solvent undergoes hydrolysis in the presence of moisture, generating hydrogen chloride and corrosive organic acids, a stabiliser package is mandatory. A typical formulation consists of 1,4‑dioxane (0.3–0.5 wt %) and a butylene‑oxide acid acceptor (0.05–0.1 wt %). Acid acceptance, expressed as NaOH equivalent per ASTM D2106, must be maintained above 0.15 wt % to forestall pitting corrosion on 316L stainless‑steel heat‑exchanger surfaces. In field operation a daily bleed‑and‑feed of concentrated stabiliser solution, coupled with on‑line conductivity monitoring of water‑separator condensate, keeps the pH above 6.5. Failure to control acidity has resulted in through‑wall corrosion of evaporator coils within 800 h of continuous service at a chemical processing facility. Contact with aluminium, magnesium or zinc fines must be rigorously excluded; accidental accumulation of aluminium swarf in the sump has provoked exothermic dehydrochlorination events that raised sump temperature above 200 °C within minutes, as documented in a Health and Safety Executive incident bulletin. Equipment materials of construction are therefore specified as 316L or Hastelloy C‑276 per ASME B31.3.

    In free‑radical polymerisation of vinylidene chloride, 1,1,1,2‑tetrachloroethane acts as a chain‑transfer agent to regulate molecular weight. The chain‑transfer constant (Cₓ) obtained by the Mayo method at 60 °C is 1.2 × 10⁻³ relative to monomer concentration; the value was determined by gel‑permeation chromatography calibrated against polystyrene standards per ISO 16014‑1:2019. The resulting low‑molecular‑weight fractions exhibit reduced melt viscosity, enabling processing on single‑screw extruders with an L/D of 25:1 without exceeding 150 °C head pressure.

    The product is supplied in 200‑L internally lacquered steel drums under a nitrogen pad of 20–50 kPa, with a maximum recommended storage period of 12 months at temperatures not exceeding 40 °C.

    In the Fluorochemical Supply Chain: Tetrachloroethane as a C2 Building Block

    Over 40 % of globally produced 1,1,1,2‑tetrachloroethane is consumed in the manufacture of 1,1,1,2‑tetrafluoroethane (R‑134a) via liquid‑phase fluorination with anhydrous hydrogen fluoride. Feed‑isomer purity must exceed 99.0 % to minimise the formation of the 1,1,2,2‑isomer, which yields undesirable pentafluoroethane (R‑125) and toxic perfluoroisobutylene under catalytic conditions. The reaction is carried out in a jacketed Hastelloy reactor at 80–90 °C and 1.5 MPa, employing antimony pentachloride as catalyst at a loading of 2–5 mol % relative to HF. Crude‑product distillation through a column of 30 theoretical plates at a reflux ratio of 3:1 delivers R‑134a of > 99.9 % purity (GC‑FID per ASTM D6806). Water impurity above 50 mg kg⁻¹ causes catalyst hydrolysis and formation of solid antimony oxyfluoride deposits that obstruct the reactor sparger, necessitating quarterly hot‑water washouts. By contrast, the alternative feedstock 1,1,2,2‑tetrachloroethane would generate symmetrical fluorinated species unsuited for thermodynamic‑cycle optimisation in mobile air‑conditioning systems.

    Occupational exposure to 1,1,1,2‑tetrachloroethane is governed by an 8‑h time‑weighted average of 1 ppm (7 mg m⁻³) under OSHA PEL (29 CFR 1910.1000) and the ACGIH TLV‑TWA, both carrying a skin notation; the NIOSH REL is identical. IARC classifies the substance as Group 2B (possibly carcinogenic to humans), while ACGIH assigns designation A3 (Confirmed Animal Carcinogen with Unknown Relevance to Humans). Biological monitoring utilises NIOSH Method 8303 for urinary trichloroethanol and trichloroacetic acid; an end‑of‑shift BEI of 30 mg L⁻¹ for trichloroacetic acid is recommended. Engineering controls must hold airborne concentrations below the TLV; capture velocities for local exhaust ventilation should be at least 0.5 m s⁻¹ at the point of vapour release, as specified in the ACGIH Industrial Ventilation Manual, 30th Edition.

    When Operating within the Constraints of REACH Annex XVII and GHS Classification

    Under Regulation (EC) No 1272/2008 (CLP), the substance carries hazard statements H315 (causes skin irritation), H319 (causes serious eye irritation), H332 (harmful if inhaled), H335 (may cause respiratory irritation), H351 (suspected of causing cancer), and H373 (may cause damage to organs through prolonged or repeated exposure), with the signal word Danger. Although not listed in REACH Annex XVII as an intrinsically restricted substance, registrants must demonstrate safe use for all exposure routes; dermal uptake can account for up to 40 % of the total body burden in professional vapour‑degreasing settings, as modelled in the Chemical Safety Report. The regulatory‑inventory status is summarised below.

    Country / RegionLegislation / InventoryStatusDetails
    United StatesTSCAActiveListed; PMN‑exempt
    European UnionREACHRegistered ≥ 1000 t a⁻¹EC No. 211‑135‑1
    JapanCSCLPriority Assessment ChemicalMITI No. 2‑92
    South KoreaK‑REACHRegisteredKE‑02324
    AustraliaAICSListed
    CanadaDSLListed