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Dichloromethane

    • Product Name: Dichloromethane
    • Factroy Site: No. 100, Qinhuai Road, Jiangning District, Nanjing, Jiangsu, China
    • Price Inquiry: sales3@ascent-chem.com
    • Manufacturer: Ascent Petrochem Holdings Co., Limited
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    Specifications
    HS Code 756172
    Product Name Dichloromethane
    Chemical Formula CH2Cl2
    Molar Mass 84.93 g/mol
    Cas Number 75-09-2
    Appearance Colorless liquid
    Odor Chloroform-like, sweet odor
    Density 1.326 g/cm3 at 20°C
    Melting Point -96.7 °C
    Boiling Point 39.6 °C
    Solubility In Water 13.2 g/L at 25°C
    Vapor Pressure 47.4 kPa at 20°C
    Refractive Index 1.4242 at 20°C
    Viscosity 0.43 mPa·s at 20°C
    Dipole Moment 1.60 D
    Flash Point None (non-flammable)

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

    Packing & Storage
    Packing Dichloromethane, 500 mL, packaged in an amber glass bottle with PTFE-lined cap, securely sealed, and labeled with hazard warnings.
    Container Loading (20′ FCL) Load 20′ FCL with securely packed UN1593 Dichloromethane drums; ensure proper labeling, ventilation, and segregation as Class 6.1 dangerous goods.
    Shipping Dichloromethane (UN1593) is a toxic, volatile chemical requiring careful shipping. Transport as Hazard Class 6.1 in sealed, corrosion-resistant containers, clearly labeled, with proper ventilation and segregation from oxidizers. Avoid heat and ignition sources. Comply with all international regulations and provide accurate documentation for land, sea, or air transport.
    Storage Store dichloromethane in a cool, dry, well-ventilated area away from direct sunlight and heat sources. Keep in a tightly closed, properly labeled container made of compatible materials, such as glass or suitable plastic. Separate from strong oxidizers, acids, and alkalis. Use local exhaust ventilation and grounded containers to minimize vapor accumulation and static discharge risks.
    Shelf Life Dichloromethane has a typical shelf life of 2–3 years when stored tightly sealed, cool, dry, and away from light.
    Application of Dichloromethane

    At 25 °C, solvent-based paint removal formulations built on dichloromethane are designed to penetrate and swell thermoset coatings rather than dissolve them; the low surface tension and high density of the solvent promote rapid wetting of vertical steel and aluminium substrates. Compliance for this downstream segment is governed by worker-exposure limits in OSHA 29 CFR 1910.1052, which sets an 8-hour time-weighted average of 25 ppm, a 15-minute short-term exposure limit of 125 ppm, and an action level of 12.5 ppm, by REACH Annex XVII Entry 59 restricting paint-stripper products containing ≥0.1 wt% dichloromethane in most professional and all consumer supply routes, and by US EPA 40 CFR Part 751 Subpart B for methylene chloride risk management. The formulation addition ratios observed in production batches centre on 65–85 wt% dichloromethane, 5–10 wt% methanol or ethanol co-solvent, 1.0–2.5 wt% paraffin wax evaporation barrier, 1.0–2.0 wt% hydroxypropyl methylcellulose or fumed silica thixotrope, and 0.5–1.5 wt% alkaline accelerator; below 55 wt% DCM, evaluations on 100 µm amine-cured epoxy drawdowns over cold-rolled steel prepared and scribed per ASTM D609-17 and ASTM D3359-17 show single-pass dwell time extends beyond 30 min, which is the upper practical limit for field application. Downstream applicators airless-spray or brush the thickened gel onto intact aged coating films, allow 10–30 min dwell under a non-porous film or vapour suppressant, and mechanically lift the swollen layer with plastic scrapers before solvent wiping and corrosion-inhibitive wash. The terminal articles generated by this segment comprise aerospace refinishing over epoxy primers, architectural metal refurbishment on curtain-wall extrusions, and marine maintenance over aged antifouling or epoxy tank coatings.

    Dichloromethane downstream compliance matrix
    Application categoryGoverning standard or ruleQuantitative thresholdAnalytical endpoint
    Paint and coating removalOSHA 29 CFR 1910.1052REACH Annex XVII Entry 59EPA 40 CFR Part 751 Subpart B25 ppm 8-h TWA; 125 ppm 15-min STEL; ≥0.1 wt% formulation restrictionFormulation GC-FID; workplace air sampling
    Pharmaceutical extractionICH Q3CUSP <467>Class 2 PDE 6 mg/day; concentration limit 600 ppmHeadspace GC-MS
    Vapour degreasingASTM D6368-17OSHA 29 CFR 1910.105240 CFR Part 63 Subpart TStabiliser package 0.2–0.5 wt%; PEL 25 ppm; moisture below 200 ppmAcid acceptance titration; IR spectroscopy; workplace sampling
    Polycarbonate synthesisFDA 21 CFR 177.1580USP <661>Organic-to-aqueous volume ratio 2.0:1–4.0:1; final solids 8–15 wt%Headspace GC-MS residual solvent; USP extraction tests
    Flexible polyurethane foamEU Directive 2010/75/EUISO 845-20062.5–8.0 php DCM; density 14–22 kg/m³Foam apparent density per ISO 845-2006
    DecaffeinationFDA 21 CFR 173.225Directive 2009/32/ECResidual DCM in roasted coffee ≤10 ppm; solvent-to-bean mass ratio 3:1–6:1AOAC headspace GC

    What Limits Residual Dichloromethane in Pharmaceutical Extraction Workflows?

    The governing residual solvent framework for dichloromethane in pharmaceutical extraction is ICH Q3C, which classifies the solvent as Class 2 with a permitted daily exposure of 6 mg/day and a concentration limit of 600 ppm; this limit is verified in finished API and excipient batches under headspace GC-MS conditions described in USP <467>. In a typical production campaign, a pH-adjusted fermentation broth or aqueous botanical extract is fed to a multistage liquid-liquid extraction skid where DCM-to-feed volume ratio is maintained between 1.0:1 and 3.0:1 across 4–6 theoretical stages; for poorly defined whole-plant matrices, percolation vessels charge 5–8 L of DCM per kilogram of dried biomass, with the solvent recycled after fractional vacuum distillation at 35–40 °C to avoid thermal degradation of temperature-sensitive alkaloid and steroid fractions. Phase separation is accomplished in Podbielniak centrifugal extractors or static decanters, and residual water is removed from the organic phase with sodium sulfate or molecular sieves before distillation; aqueous raffinate is re-extracted to recover entrained solvent below the site discharge limit. Downstream processing includes carbon polishing, antisolvent crystallisation, vacuum tray drying, and salt formation in acetone or ethanol, each of which reduces solvent content below the 600 ppm monograph limit before final API drying. Finished dosage and intermediate categories span macrolide antibiotic intermediates, semi-synthetic corticosteroid APIs, and purified alkaloid salts used in anticholinergic or antispasmodic dosage forms; the DCM extraction step is specifically avoided for low-boiling APIs that crystallise from water, because DCM-water azeotrope handling complicates recovery.

    When a vapour degreasing line using dichloromethane is operated with a freeboard ratio above 0.75 and moisture ingress below 200 ppm, the boiling sump stabilises at 39.8 °C, and stainless 316L surgical blanks are cleaned and dried within 3–10 min without flash-rust formation. Compliance for this sector rests on vapour-degreasing-grade solvent specifications in ASTM D6368-17, halogenated solvent cleaning NESHAP emission controls in 40 CFR Part 63 Subpart T, and the 25 ppm 8-hour PEL and 125 ppm 15-minute STEL in OSHA 29 CFR 1910.1052. The liquid formulation is not an end-use product but a stabilised solvent bath in which DCM comprises 99.5–99.8 wt% and the remaining 0.2–0.5 wt% consists of acid acceptor packages—usually epoxide species such as butylene oxide or propylene oxide—plus a metal inhibitor below 0.05 wt%; acid acceptance is titrated weekly because chlorides generated by thermal decomposition or water hydrolysis accumulate and attack aluminium 6061 and bronze components. A production-sized open-top degreaser maintains four functional zones: a boiling sump at 39.8 °C for heavy soil, an ultrasonic immersion chamber, a cool rinse sump for particulate carryover, and a vapour zone where condensing solvent on the part removes residual film; condenser water is held at 5–10 °C to maintain freeboard stability, and the primary condenser exhaust is routed to activated carbon beds or thermal oxidation because DCM is a VOC subject to NESHAP solvent cleaning emission limits. Parts are retained in the vapour blanket until surface temperature equals vapour temperature, then withdrawn through a freeboard zone above the primary condenser. Components cleaned in these lines are subsequently installed as surgical instruments, oxygen-system valve bodies, precision bearing assemblies, and aluminium heat-exchanger components in avionics cooling loops; high-magnesium and high-copper aluminium alloys are excluded unless inhibitor concentration is increased and water content is held below 100 ppm.

    Whenever Methylene Chloride Replaces Other Halogenated Solvents in Interfacial Polycarbonate Polymerisation

    Interfacial polycondensation of bisphenol A and phosgene uses dichloromethane as the chlorinated organic phase because the solvent dissolves oligomeric carbonate chains while remaining phase-separated from an aqueous caustic stream. In production reactors, the DCM-to-aqueous phase volume ratio is maintained between 2.0:1 and 4.0:1 to keep sodium chloride salt concentration in the aqueous phase below the salting-out threshold and maintain interfacial clarity, and the final polycarbonate solution is controlled at 8–15 wt% resin solids before washing. The aqueous caustic phase carries a 5–10 wt% sodium hydroxide excess, and phosgene addition is regulated by online pH and redox probes; exceeding pH 12 hydrolyzes phosgene to carbonate and lowers yield, while dropping below pH 9.5 promotes oligomer chain termination. The process operates at pH 10.5–11.5 and 20–35 °C, with phosgene gas introduced through Hastelloy C-276 dip pipes into glass-lined or PTFE-lined reactors; triethylamine catalyst is charged at 1–3 mol% relative to bisphenol A, and p-tert-butylphenol chain stopper at 1–5 mol% is adjusted to target a weight-average molecular weight of 28,000–35,000 g/mol for optical and medical grades. After phase separation, the organic layer is washed sequentially with dilute hydrochloric acid and deionised water, then fed to steam precipitation or a devolatilising twin-screw extruder at 280–300 °C to strip solvent and generate free-flowing pellets. Compliance standards include FDA 21 CFR 177.1580 for polycarbonate resins intended for food-contact articles and USP <661> for plastic packaging components; resin lots destined for pharmaceutical containers are subjected to extractables testing rather than a fixed DCM residual limit, because the polymer monograph controls total migration in the finished article. The resulting resin grades are converted into optical disc substrates, automotive headlamp lenses, medical device housings, and reusable water bottles.

    Continuously, on slabstock flexible polyurethane foam lines, methylene chloride is metered into the polyol preblend before the high-shear mixhead to supplement carbon dioxide as a physical-blowing agent; the latent heat of vaporisation of 329 kJ/kg absorbs exothermic polymerisation energy and stabilises cell walls during the critical gel phase. Dosage is set between 2.5 and 8.0 parts by weight per 100 parts polyol, with water at 3.5–5.0 php, toluene diisocyanate index 105–115, and tin/amine catalyst combined at 0.1–0.5 php; foam density then falls into the 14–22 kg/m³ range when measured by ISO 845-2006. The polyol blend is cooled to 18–22 °C before entering a high-shear mixhead at 3,500–5,500 rpm, after which the reacting liquid is poured onto a moving conveyor, rises for 90–180 s, and cures as a continuous block for 24–72 h before slitting. Ventilation and VOC abatement fall under EU Directive 2010/75/EU, and worker exposure is capped by OSHA 29 CFR 1910.1052; DCM loadings above 10 php are known to depress centre-block exotherm below 120 °C, producing open-cell shrinkage, cold cure bands, and discolouration in blocks thicker than 0.8 m, so higher loadings are confined to thin pour geometries with forced-air cross-flow. Slit blocks and die-cut shapes from this process enter low-density furniture and mattress foam, acoustic panel substrates, carpet underlay, and automotive seating base stock.

    Diffusion-Controlled Decaffeination in Packed-Bed Extraction Columns

    Green coffee beans are hydrated to 20–30 wt% moisture and preheated to 35–40 °C before countercurrent contact with food-grade dichloromethane in a packed-bed extraction battery; caffeine transfer is governed by aqueous-phase diffusion through the swollen bean matrix rather than by solvent molarity alone. FDA 21 CFR 173.225 authorises dichloromethane as a direct extraction solvent for decaffeinated coffee and sets the residual limit in roasted coffee at ≤10 ppm; in the EU, extraction solvent use is controlled under Directive 2009/32/EC, with residue verification required on finished roast-and-ground lots. Typical continuous extraction lines run a solvent-to-bean mass ratio of 3:1–6:1 per pass, with 4–8 passes or equivalent countercurrent stages over a 3–5 h contact window, and circulation flow is held at 2–5 bed volumes per hour; published data for roaster-specific commercial cycles is limited because solvent ratios are adjusted to green bean moisture, cultivar density, and target caffeine reduction below 0.1 wt% in the roasted bean. After extraction, the beans are steam-purged in a desorber to remove residual DCM, dried under vacuum to 11–12 wt% moisture, and roasted according to product specification; solvent from the loaded liquor is recovered by fractional distillation at 40–60 °C under nitrogen blanketing to avoid oxygen ingress and acid formation. End-use formats from this extraction route are decaffeinated whole-bean and roast-and-ground coffee, instant coffee intermediates, and decaffeinated tea extract solids.

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    Certification & Compliance
    More Introduction

    Industrial dichloromethane (DCM, CAS 75-09-2) is supplied as a low-boiling chlorinated solvent with a normal boiling point of 39.6 °C, a liquid density of 1.326 g/cm³ at 20 °C, and a vapour pressure of 46.5 kPa at 20 °C. The product is manufactured principally by thermal chlorination of methyl chloride or methane; reactor effluent containing unreacted methyl chloride, methylene chloride, chloroform, and carbon tetrachloride is separated by staged distillation. Commercial product specifications under ASTM D4701 distinguish technical, vapour degreasing, stabilised urethane, and extraction grades by assay, water content, acidity as hydrogen chloride, nonvolatile residue, colour on the platinum-cobalt scale, and free halogen content. A typical vapour degreasing grade is released with a minimum assay of 99.9%, water below 0.02%, acidity as HCl below 0.001%, and nonvolatile residue below 0.001%. Stabiliser identity and concentration are disclosed in the supplier safety data sheet and vary with expected exposure to water, light, and reactive metal salts. Solvency is expressed by a Kauri-butanol value of 136, which is higher than many ketone and ester alternatives. The solvent does not exhibit a flash point under standard closed-cup methods, but the high vapour pressure requires sealed transfer and refrigerated condenser systems in open-topped equipment.

    In closed-loop equipment operating at sump temperatures between 25 °C and 35 °C, DCM remains below its boiling point while vapour-zone temperatures remain near 39.6 °C; this provides a narrow but technically defined processing window for heat-sensitive copper, brass, aluminium, zinc, and electronic assemblies. The liquid density of 1.326 g/cm³ and surface tension of approximately 28.12 mN/m at 20 °C assist penetration beneath fine-pitch components and promote ultrasonic cavitation energy transfer in tanks operating at 25–40 kHz. Acid acceptance is the principal product-control parameter because DCM hydrolyses slowly in the presence of water and can release hydrogen chloride. Stabiliser packages containing cyclohexane, amylene, or substituted phenolic compounds are added in low parts-per-million concentrations to absorb acidic decomposition products. Production-scale vapour degreasers exhibit increased corrosion of aluminium and zinc workpieces when the acidity of the sump liquid exceeds 0.001% as HCl; titration under ASTM D2989 is used to monitor the acid acceptance reserve. Maintenance procedures include draining, distillation, and restabilisation when the reserve is exhausted. Freeboard height, lip ventilation, and cooling-coil capacity must be validated against the 25 ppm 8-hour OSHA permissible exposure limit under 29 CFR 1910.1052.

    Extraction of temperature-labile pharmaceutical intermediates with DCM is performed in closed-loop stirred extractors, liquid-liquid centrifugal separators, and wiped-film evaporators. The solvent is selected when the target molecule partitions preferentially into the chlorinated phase and when distillative recovery at 39.6 °C reduces thermal degradation of the active. Residual DCM in drug products is controlled under ICH Q3C Class 2 with a permitted daily exposure of 6.0 mg/day and a concentration limit of 600 ppm; release testing uses gas chromatography with headspace sampling calibrated against reference standards. Because water solubility is approximately 13.2 g/L at 25 °C, wet-washing steps can retain DCM in the aqueous phase if temperature and phase ratios are not controlled. Drying with sodium sulfate or molecular sieves prior to distillation reduces water-induced hydrolysis. Published batch-to-batch extraction efficiency data from production-scale centrifugal extractors are limited to equipment-specific qualification studies.

    Does Dichloromethane Provide a Non-Flammable Processing Window for Metal Degreasing?

    Defluxing of printed circuit assemblies with DCM is limited by compatibility with epoxy-glass laminates, component markings, and conformal coatings. The low boiling point reduces thermal stress on solder joints, but the solvent may attack some acrylic and rubber-based markings. The combination of high density and low surface tension permits penetration beneath fine-pitch components, while ionic residues are removed only if the rinse stage uses fresh distilled solvent. Enclosed defluxing systems with solvent recovery are required because the airborne concentration limit is low. Stainless steel, polytetrafluoroethylene, polyvinylidene fluoride, and high-density polyethylene are generally acceptable for continuous contact; EPDM, neoprene, and nitrile rubber are not specified for continuous immersion because swelling and extractable contamination can occur. Published data for specific compounded elastomer grades are limited, and immersion testing per manufacturer protocols is required before long-term equipment service.

    Paint stripping formulations containing DCM are applied at ambient temperature to crosslinked alkyd, epoxy, polyurethane, and moisture-cured urethane coatings. The solvent penetrates the film and reduces inter-coat adhesion, allowing mechanical removal with scrapers or low-pressure water. Coating removal rate can be compared using ASTM D6189; test panels are exposed under controlled film thickness and temperature. Regulatory restrictions rather than solvency now define the application boundary. Under REACH Annex XVII Entry 59, paint strippers containing DCM at or above 0.1% by weight cannot be supplied to general consumers; professional use requires training and controlled ventilation. Workplace exposure must remain below the 25 ppm 8-hour OSHA permissible exposure limit, with an action level of 12.5 ppm triggering periodic monitoring and medical surveillance under 29 CFR 1910.1052. Carbon monoxide elimination as a metabolite and central nervous system depression require air-supplied respiratory protection when airborne concentrations exceed cartridge-based organic vapour respirator limitations.

    Replacement of DCM with methyl ethyl ketone, acetone, or toluene in ambient cleaning is complicated by flammability. MEK has a closed-cup flash point of -6 °C and an OSHA 8-hour permissible exposure limit of 200 ppm; acetone has a closed-cup flash point of -18 °C and an OSHA permissible exposure limit of 1000 ppm; toluene has a closed-cup flash point of 4 °C and an OSHA permissible exposure limit of 200 ppm. DCM is therefore retained where non-flammability and high solvency are simultaneous requirements, but the lower occupational exposure limit and regulatory status require automated handling, continuous monitoring, and sealed transfer.

    When Dichloromethane Replaces Trichloroethylene in Closed-Loop Degreasing Operations

    Direct substitution of trichloroethylene by DCM in a vapour degreaser is not a drop-in change because the boiling point falls from 87.2 °C to 39.6 °C and vapour pressure rises from approximately 8.1 kPa to 46.5 kPa at 20 °C. The lower boiling point reduces heat load on immersion heaters, but the higher vapour pressure increases solvent loss through idling diffusion and requires a deeper freeboard ratio, lower freeboard temperature, and higher-capacity refrigerated condensers. Solvation behaviour also changes: DCM’s Kauri-butanol value of 136 is higher than trichloroethylene’s typical 130, which improves removal of high-molecular-weight oily soils but may attack polymer seals, elastomer gaskets, and wire insulations that were compatible with trichloroethylene. The density difference between DCM (1.326 g/cm³) and trichloroethylene (1.464 g/cm³) affects ultrasonic cleaning mechanics and sludge settling; DCM’s lower density reduces settling velocity of solid fines, which can increase the burden on filtration and distillation stills. Exposure limits also differ: the OSHA 8-hour permissible exposure limit for DCM is 25 ppm, while the OSHA permissible exposure limit for trichloroethylene is 100 ppm and for perchloroethylene is 100 ppm. Carbon-bed adsorption systems sized for trichloroethylene vapour pressure must be revalidated for DCM because a higher vapour pressure at equivalent airflow shortens breakthrough time.

    Property Dichloromethane Trichloroethylene Perchloroethylene Methyl ethyl ketone
    Boiling point at 1 atm (°C) 39.6 87.2 121.2 79.6
    Density at 20 °C (g/cm³) 1.326 1.464 1.623 0.805
    Vapour pressure at 20 °C (kPa) 46.5 8.1 1.9 10.5
    Kauri-butanol value 136 130 90 105
    OSHA 8-hour permissible exposure limit (ppm) 25 100 100 200
    Closed-cup flash point (°C) none none none -6

    Storage of bulk DCM in carbon steel requires moisture exclusion and a nitrogen pad or desiccant vent because liquid-phase water above 0.02% accelerates hydrolysis and hydrogen chloride generation. Floating suction lines and submersible pumps reduce vapour release; tanks are grounded and bonded. In chemical synthesis, DCM is used as an extraction and reaction solvent for quaternisation and phase-transfer-catalysed alkylation; process equipment is specified for the boiling point of 39.6 °C and the weak hydrolysis tendency. In analytical laboratories, DCM is used for liquid-liquid extraction of semivolatile organic compounds under US EPA Method 3510C; trace analysis requires lot-certified high-purity solvent with nonvolatile residue below 1 mg/L to avoid interference with gas chromatographic detection. Published data for specific production-scale configurations are limited, particularly where proprietary stabiliser packages alter acid acceptance and equipment compatibility.

    Framework Relevant provision or limit Application boundary
    29 CFR 1910.1052 8-hour permissible exposure limit 25 ppm; short-term exposure limit 125 ppm; action level 12.5 ppm Workplace exposure to methylene chloride
    REACH Annex XVII Entry 59 Supply to general public restricted for paint strippers containing ≥0.1% DCM European Union market
    ICH Q3C Class 2 Permitted daily exposure 6.0 mg/day; concentration limit 600 ppm Residual solvent in pharmaceutical products
    ASTM D4701 Specification for assay, water, acidity, nonvolatile residue, colour, free halogens Product release testing for DCM grades
    US EPA 40 CFR 751 TSCA section 6 risk management rule for methylene chloride; workplace chemical protection requirements and use restrictions United States manufacturing, processing, and distribution

    Replacement of perchloroethylene in low-temperature immersion stripping with DCM is technically feasible only when the higher vapour pressure of 46.5 kPa at 20 °C is managed by sealed lids, freeboard refrigeration, and continuous monitoring. Perchloroethylene’s lower vapour pressure of 1.9 kPa at 20 °C gives lower idling losses but longer drying times at its boiling point of 121.2 °C. DCM’s lower boiling point permits evaporation at 39.6 °C, which reduces heat exposure to temperature-sensitive substrates but increases the refrigeration load. The higher Kauri-butanol value of DCM, 136 versus perchloroethylene’s typical 90, allows removal of crosslinked soils that perchloroethylene cannot dissolve; however, the stronger solvency also reduces compatibility with some plastic fixtures and maskants. Published data for this specific substitution in production-sized degreasers are limited to process-specific validation studies.