| HS Code | |
| Product Name | Dichloromethane |
| Chemical Formula | CH2Cl2 |
| Iupac Name | Dichloromethane |
| Cas Number | 75-09-2 |
| Molar Mass | 84.93 g/mol |
| Appearance | Colorless liquid |
| Odor | Ether-like, sweet |
| Density | 1.3266 g/cm3 at 20 C |
| Melting Point | -96.7 C |
| Boiling Point | 39.6 C |
| Solubility In Water | 13 g/L at 20 C |
| Vapor Pressure | 47.4 kPa at 20 C |
| Refractive Index | 1.4244 at 20 C |
| Flash Point | None |
| Autoignition Temperature | 556 C |
| Viscosity | 0.44 mPa·s at 20 C |
As an accredited Dichloromethane factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | Dichloromethane packaged in 25 L UN-rated steel drums, sealed with secure closures, hazard labels, and clear chemical identification. |
| Container Loading (20′ FCL) | Container loading (20′ FCL) for Dichloromethane: palletized UN-approved drums, Class 6.1, UN1593, securely stowed/lashed, labeled, with dangerous goods documentation. |
| Shipping | Dichloromethane (methylene chloride) ships as UN1593, Hazard Class 6.1, Packing Group III. Use UN-approved packaging with toxic labels, correct shipping papers, and markings. Transport in cool, ventilated areas away from ignition/heat; keep containers closed and avoid inhalation exposure. Follow applicable DOT, IMDG, and IATA regulations. Handle as a hazardous material. |
| Storage | Dichloromethane: store in a cool, dry, well-ventilated area away from direct sunlight, heat, and ignition sources. Keep containers tightly closed, upright, and clearly labeled. Use secondary containment in a locked, dedicated chemical cabinet if required. Separate from strong oxidizers, acids, bases, and reactive metals. Avoid breathing vapors. Ensure adequate ventilation, use appropriate personal protective equipment, and follow local regulations. |
| Shelf Life | Dichloromethane is stable under recommended storage; shelf life is 2–5 years when kept sealed, cool, dry, and away from light. |
In pharmaceutical downstream processing, dichloromethane functions as a water-immiscible organic extractant in continuous centrifugal liquid-liquid trains where thermolabile intermediates require solvent removal below 40 °C. The solvent’s density of 1.33 g/cm³ at 20 °C and interfacial tension against brine permit rapid phase disengagement in Podbielniak centrifugal extractors and disc-stack separators. Typical extraction sequences for macrolide antibiotics, steroids, and vitamin intermediates use DCM as the heavy or light phase depending on brine concentration; phase ratio is not fixed and is adjusted after measuring distribution coefficients in laboratory shake-out and pilot partition runs. Recovery is conducted in falling-film evaporators or thin-film dryers under mild vacuum at 35–40 °C, which protects oxidation-prone APIs from thermal degradation. Residual methylene chloride in the final drug substance is governed by ICH Q3C(R8) as a Class 2 solvent with a permitted daily exposure of 6 mg/day and a concentration limit of 600 ppm. Finished API batches are analysed by headspace gas chromatography with flame ionisation detection according to USP 467 Procedure A. Production-scale dryers show batch-to-batch residual variance when static tray vacuum drying is used for crystalline filter cakes; rotating paddle dryers and double-cone dryers reduce channeling and lower residual solvent by improving heat transfer and surface renewal. Wetted parts are specified in 316L stainless steel or Hastelloy C-276 when chloride salts are present, because DCM can hydrolyse slowly at elevated temperatures in the presence of free water and release hydrogen chloride. Operational boundaries include avoidance of strong bases and primary or secondary amines, which can react exothermically with dichloromethane, and moisture control in recovered solvent tanks to prevent acid-catalysed degradation. Published data for distribution ratios of proprietary API extraction trains are limited, so laboratory shake-out studies and pilot centrifugal runs are required for each new molecule.
| Application | Governance or test method | Numerical limit | Analytical or field procedure |
|---|---|---|---|
| Pharmaceutical residual solvent in drug substance | ICH Q3C(R8) Class 2; USP 467 | PDE 6 mg/day; concentration limit 600 ppm | Headspace GC-FID, USP 467 Procedure A |
| Vapor degreasing occupational air, United States | OSHA 29 CFR 1910.1052 | PEL 25 ppm 8-hour TWA; STEL 125 ppm | Charcoal tube personal sampling, GC-FID |
| Vapor degreasing occupational air, ACGIH | ACGIH TLV/BEI | TLV 50 ppm 8-hour TWA | Personal sampling pump, GC-FID |
| Residual solvent in decaffeinated roasted coffee, United States | 21 CFR 173.228 | 10 ppm DCM in roasted coffee | Headspace GC after moisture adjustment |
The interfacial phosgenation route to polycarbonate relies on methylene chloride as the organic phase dissolving oligomeric chains and polymer that forms at the aqueous-organic interface. The reaction is maintained at pH 10–11 by metered sodium hydroxide, and the reactor temperature is kept between 20 °C and 30 °C to avoid phosgene decomposition and undesired hydrolysis. Glass-lined production reactors from 10,000 L to 40,000 L are equipped with multi-stage turbine impellers and baffles; dispersion behaviour, interfacial area, and organic-phase viscosity change as molecular weight increases. Molecular weight is regulated by end-capping with a monofunctional phenol and by controlling the organic-to-aqueous phase ratio. When the DCM phase becomes too viscous or the dispersion inverts, interfacial mass transfer of phosgene into the aqueous phase becomes irregular and molecular weight distribution broadens. Viscosity numbers are measured in methylene chloride at 25 °C using dilute-solution viscometry according to ISO 1628-4:2015; the specification target depends on the grade and is converted to melt flow rate afterwards using ISO 1133-1:2022. Solvent recovery from the polymer solution is carried out by steam stripping and decantation, followed by drying of wet polymer crumb. Residual DCM in pellets must be controlled for food-contact grades under relevant national regulations. Process experience indicates that insufficient solvent volume causes the polymer-rich phase to invert into a high-viscosity continuous organic gel, increasing agitator torque and reducing phosgene consumption efficiency; excess solvent reduces throughput and raises recovery load. The glass transition temperature of the final polycarbonate is not directly influenced by DCM residual at normal drying levels, but retained solvent can generate microvoids during injection moulding if pellet pre-drying is incomplete.
For ferrous alloys, copper alloys, and selected aluminium components, open-top vapour degreasing with dichloromethane is specified when stabilizer concentration and moisture content are both controlled. The solvent boils at 39.6 °C, and its low surface tension of approximately 28 mN/m at 20 °C provides penetration into blind holes and close-tolerance assemblies. A typical batch vapour degreaser consists of a boiling sump, an ultrasonically agitated immersion section, a condensation zone maintained by cooling coils, and a freeboard section; operating practice follows ASTM D3698 for solvent vapour degreasing operations. Proprietary stabilizer packages, often acid acceptors based on epoxide or oxide chemistry, are maintained at concentrations specified by the solvent supplier to neutralise hydrolysis-derived hydrogen chloride. Water ingress from part drag-out or humid air is the dominant production risk; water separators and desiccant loops are installed to keep water below the stabiliser neutralisation breakpoint. When stabilizer depletion occurs, the solvent becomes acidic and can corrode aluminium parts and stainless steel sump walls, producing soluble metal chlorides that contaminate surfaces. Occupational exposure is controlled under OSHA 29 CFR 1910.1052 with a permissible exposure limit of 25 ppm as an 8-hour time-weighted average and a short-term exposure limit of 125 ppm; ACGIH lists a threshold limit value of 50 ppm as an 8-hour TWA. Carbon adsorption and refrigeration condensers recover solvent from the vapour zone and reduce emissions. DCM is nonflammable under normal vapour degreasing conditions, but thermal decomposition in a fire or on ignition sources can generate hydrogen chloride and traces of phosgene; therefore heating elements are specified with temperature interlocks. Magnesium and reactive aluminium fines are incompatible with DCM vapour degreasing because finely divided metal can react with chlorinated solvent under specific conditions.
Flexible slabstock polyurethane lines use methylene chloride as an auxiliary physical blowing agent metered into the polyol preblend, where the exothermic isocyanate-water reaction raises block core temperature to 140–160 °C. The solvent boils at 39.6 °C, vaporises in the rising foam, and supplements carbon dioxide from the water reaction to lower apparent density. DCM loadings in slabstock formulations commonly range from 2 php to 8 php; the exact level depends on desired core density, block height, and the water level in the formulation. At higher loadings, the endothermic vaporisation of DCM reduces block temperature, delays urea and urethane gelation, and plasticises cell struts, which can result in foam collapse, internal splits, or coarse cell structure. Production lines use high-pressure metering units and multistream mixheads from slabstock equipment manufacturers, with laydown onto an inclined trough and continuous side paper feeds. Blocks of 0.8 m to 1.2 m height are cured at ambient temperature before cutting. Apparent core density is measured according to ISO 845; tensile, elongation, and tear properties are evaluated under ASTM D3574-17 Test E and Test F. Because DCM lowers the density without contributing to polymer formation, formulators compensate by adjusting the isocyanate index, typically in the 105–115 range for flexible slabstock grades, to maintain load-bearing and resilience. Batch-to-batch variance in DCM metering at the mixhead directly changes core density and hardness, so mass flow meters are calibrated against the solvent’s density of 1.33 g/cm³ at 20 °C. Operational boundaries include avoiding excessive DCM above the formulation-specific stability limit and controlling ventilation around block storage because residual DCM continues to diffuse from the foam during cure. DCM is not used in moulded foam lines with closed moulds where the exotherm and venting conditions differ and where solvent retention can cause demoulding defects.
For optical-grade cellulose triacetate film casting, dichloromethane serves as the primary dope solvent in a blended solvent system with methanol. The low boiling point of 39.6 °C allows controlled evaporative casting from a slot die onto a stainless steel belt, forming a film with optical retardation and thickness uniformity controlled by die lip gap and solvent partial pressure in the casting chamber. DCM dissolves cellulose triacetate at solids loadings of 15–25 wt%; methanol shortens the cloud point and modifies dope viscosity. Filtration through 5–10 μm metal fibre filters removes gels before casting. Solvent-laden air is recovered through carbon beds and condensation. Residual solvent is reduced by multi-zone drying at temperature ramps below film deformation threshold. Production experience shows that high humidity in casting rooms causes rapid evaporative cooling and moisture condensation on the cast film, producing surface defects; casting chambers are therefore operated under dew point control. Cellulose triacetate film is used in polarising plate protective layers, photographic film base, and display components. Analytical specifications include haze, thickness tolerance, and residual solvent concentration; relevant test methods are published by film manufacturers.
Solvent cement for cast acrylic, extruded acrylic, and certain polycarbonate or ABS joints is formulated with methylene chloride as the primary fast-evaporating carrier because its boiling point of 39.6 °C and vapour pressure of approximately 47 kPa at 20 °C produce open times of 15–60 s at 23 °C and 50% RH. The cement usually contains 10–20 wt% acrylic resin or polymer in place of monomer, and viscosity is adjusted to 150–500 mPa·s with a Brookfield viscometer at 25 °C. DCM dissolves the surface layers of the thermoplastic, creating an interpenetrating zone that solidifies as the solvent evaporates; joint strength depends on surface preparation, capillary fill, and the absence of solvent trapping. Tensile shear strength of rigid plastic lap joints can be tested under ASTM D3163, although published data for specific acrylic cements vary with resin type, bond line thickness, and conditioning. Bond line thickness is typically controlled between 0.05 mm and 0.25 mm; thick bond lines retain solvent and show reduced strength. DCM is distinguished from acetone by higher density, lower flammability, and more aggressive solvency for polycarbonate and acrylic, but it also attacks many engineering thermoplastics and must not be used with polyethylene, polypropylene, or nylon parts. Industrial adhesive operations require local exhaust ventilation because the solvent’s occupational exposure limit is 25 ppm under OSHA 29 CFR 1910.1052. Amine-functional additives are avoided because they can react with DCM and generate corrosive by-products. Solvent cement containing DCM is not suitable for direct food-contact surfaces or for bonding components that cannot be vented during cure.
In direct solvent decaffeination, green coffee beans are steamed and moistened, then contacted with methylene chloride in countercurrent fixed-bed extraction vessels to remove caffeine while retaining much of the bean matrix. The process is differentiated from supercritical CO2 decaffeination by lower capital cost and high caffeine selectivity, but it can co-extract some waxes and flavour precursors. Moisture content of green beans is raised before extraction to improve mass transfer, and DCM is recirculated through the bed at a controlled temperature below the point of excessive wax extraction. After extraction, beans are steamed to strip residual DCM, dried to original moisture, and roasted. United States regulation 21 CFR 173.228 permits methylene chloride as a decaffeination solvent and sets a residual limit of 10 ppm in roasted coffee. Analytical verification is performed by headspace gas chromatography with flame ionisation detection after moisture adjustment and sample comminution. Coffee processing lines install carbon adsorption and solvent recovery condensers on stripping vents to limit emission and operator exposure; personal monitoring follows OSHA 29 CFR 1910.1052 with an 8-hour TWA of 25 ppm. Decaffeinated coffee produced with DCM retains high caffeine-removal efficiency but can show batch-dependent changes in cup profile because methylene chloride extracts non-trigonelline flavour-active compounds; process control therefore uses fixed solvent-to-bean ratio and extraction time rather than residual caffeine alone. Published data for continuous countercurrent decaffeination equipment configurations are limited, so scale-up from pilot fixed-bed tests requires bean bed pressure-drop measurement and solvent flow distribution checks.
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Dichloromethane (methylene chloride, CAS 75-09-2) is a chlorinated C1 solvent with molar mass 84.93 g/mol, boiling point 39.6 °C at 101.3 kPa, density 1.3266 g/cm³ at 20 °C, and aqueous solubility 13 g/L at 25 °C. Commercial supply is differentiated by grade rather than by molecular variation: technical, vapour degreasing, urethane, ACS reagent, and pharmaceutical extraction grades are the principal designations. Each grade is delimited by purity, water, acidity, nonvolatile residue, and stabilizer package. The solvent is used in closed-loop pharmaceutical extraction, metal cleaning, polymer processing, and laboratory applications where a low boiling point and high Kauri-butanol solvency of approximately 136 allow separation from high-boiling residues. Regulatory exposure limits under 29 CFR 1910.1052 are 25 ppm 8-hour TWA and 125 ppm STEL, with an action level of 12.5 ppm.
Acceptance criteria for technical-grade material are structured around ASTM D4701-00(2020) and supplier certificate-of-analysis practices. Gas chromatography with thermal conductivity detection measures purity; Karl Fischer titration according to ASTM E203 quantifies water; acidity is titrated as HCl; nonvolatile residue is determined by evaporation at 105 °C; colour is measured against platinum-cobalt standards under ASTM D1209. Representative technical-grade acceptance values are listed in the table below. Vapour degreasing grades are further distinguished by acid-acceptor stabilizer packages designed to scavenge HCl during thermal cycling. Urethane-grade material is controlled for iron and chlorides because residual metals interfere with tin catalysts in polyurethane slabstock systems. ACS reagent grade limits residue and acidity for trace analysis.
| Property | Method | Representative limit |
|---|---|---|
| Purity | ASTM D4701-00(2020) | ≥ 99.5 wt% |
| Water | ASTM E203 | ≤ 0.020 wt% |
| Acidity as HCl | Acid acceptance titration | ≤ 0.001 wt% |
| Nonvolatile residue | Evaporation at 105 °C | ≤ 0.002 wt% |
| Iron | Supplier photometric method | ≤ 0.0001 wt% |
| Colour | ASTM D1209 | ≤ 10 APHA |
In an open-top vapour degreaser with a stainless steel 316L sump, primary coil coolant at 4 °C, and freeboard ratio of at least 1.0, stabilized dichloromethane forms a vapour zone at the boiling point. Vapour density of 2.93 relative to air retains the solvent layer, while surface tension of approximately 28.1 mN/m at 20 °C allows penetration into low-clearance geometries. Immersion baskets and ultrasonic transducers at 25–40 kHz are used for tenacious soils. Water contamination from incoming parts is removed by continuous decanting because water forms a low-boiling heteroazeotrope that raises sump temperature and accelerates hydrolysis. Compliance with 40 CFR Part 63 Subpart T requires cover design, freeboard ratio, and carbon adsorption or condensation controls; solvent-carrying pumps, shaft seals, and condensate lines on production lines are specified with 316L wetted surfaces because carbon steel pits at the vapour-liquid interface when acid acceptance is lost.
Stabilizer depletion in vapour degreasers is monitored because thermal and oxidative breakdown of dichloromethane can generate hydrogen chloride. Acid formation in the sump is measured by acid acceptance titration according to supplier methods; a drop below the maintenance threshold is indicated by pH shift in the water separator or copper mirror test failure. Production-scale failure modes include pitting of carbon steel components and etching of aluminium fixturing. Stainless steel 316L is specified for tanks, pump housings, and heat exchanger tubing. Elastomer seals are limited to fluoropolymer or ethylene-propylene diene monomer materials screened according to ISO 1817; published compatibility data for specific compound formulations should be obtained from the seal supplier. When acid acceptance falls, the solvent is either replenished with a stabilizer concentrate or replaced. Continued operation without stabilizer can produce hydrochloric acid concentrations above 0.001 wt% in the sump, and aluminium or galvanized contact is excluded because of corrosion and possible exothermic reactions.
For active pharmaceutical ingredient manufacturing, closed-loop extractors using dichloromethane are operated below 40 °C to limit thermal degradation and to reduce vacuum demand during solvent recovery. Residual solvent in drug product is controlled to 600 ppm under ICH Q3C as a Class 2 solvent; USP <467> references headspace gas chromatographic procedures for verification. Process equipment includes glass-lined reactors, PTFE-lined seals, and shell-and-tube condensers with cooling water at 6–10 °C. Solvent recovery is completed by batch distillation under reduced pressure, with a reflux ratio of 2:1 to 4:1 in structured packing columns. Aqueous layers are separated before redistillation because water lowers extraction efficiency and increases hydrolysis byproducts. Published data for specific extraction yield configurations is limited; batch records establish recovery efficiency based on the target molecule partition coefficient rather than a universal solvent-to-feed ratio. In decaffeination and natural product fractionation, residual solvent removal depends on vacuum stripping and steam sparging, not solely on distillation endpoint.
Relative to trichloroethylene and perchloroethylene, dichloromethane has a lower boiling point and a higher vapour pressure, which shortens cycle time but raises emission-control burden. The following table compiles physical data used for substitution screening.
| Property | Dichloromethane | Trichloroethylene | Perchloroethylene | n-Propyl bromide |
|---|---|---|---|---|
| Boiling point at 101.3 kPa | 39.6 °C | 87.2 °C | 121.1 °C | 71.0 °C |
| Vapour pressure at 20 °C | 47.1 kPa | 7.7 kPa | 1.9 kPa | 14.6 kPa |
| Kauri-butanol value | 136 | 129 | 90 | 125 |
| Surface tension at 20 °C | 28.1 mN/m | 29.3 mN/m | 32.3 mN/m | 25.9 mN/m |
| Aqueous solubility at 25 °C | 13 g/L | 1.1 g/L | 0.15 g/L | 0.25 g/L |
In adhesive removal and paint-stripping applications, the high solvency of dichloromethane toward acrylics, cellulose esters, and epoxy films produces fast failure of crosslinked coatings. Unlike acetone, it is not miscible with water, and its higher density causes phase separation in water-based rinses. Compared with n-propyl bromide, dichloromethane has a lower boiling point but is not a brominated compound. Process selection requires evaluation of worker exposure under 29 CFR 1910.1052 and equipment leak-tightness. Elastomer swell data for nitrile rubber show excessive volume increase; ethylene-propylene diene monomer and polytetrafluoroethylene are preferred, and screening follows ISO 1817. Metal cleaning with dichloromethane is generally unsuitable for aluminium or galvanized substrates because of corrosion risk, whereas stabilized chlorinated systems are routinely applied to 316L, carbon steel, and copper alloys.
At process boundaries, moisture exclusion and thermal exposure control are mandatory. Water contamination above 0.020 wt% in closed storage accelerates hydrolysis and phase splitting; storage tanks are fitted with desiccant breathers or nitrogen blankets at 0.5–1.0 kPa overpressure. Dichloromethane is not classified as flammable under GHS at ambient pressure, but autoignition temperature is approximately 556 °C and high-temperature operations must exclude open flames. Contact with strong bases, active metals, and aluminium fines can generate heat or chloromethane byproducts; stainless steel 316L or lined carbon steel is specified. REACH Annex XVII entry 59 restricts paint-stripper formulation in the EU unless an authorization or derogation applies. Exposure monitoring uses detector tubes or photoionization detectors calibrated against 29 CFR 1910.1052 action level of 12.5 ppm.