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Methylene Chloride Foam Blowing Agent
- Product Name: Methylene Chloride Foam Blowing Agent
- Factroy Site: Binhai New Area, Tianjin, China
- Price Inquiry: sales4@ascent-chem.com
- Manufacturer: Ascent Petrochem Holdings Co., Limited
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- In terms of specification, Methylene Chloride Foam Blowing Agent is supplied with a purity of ≥99.9% and a water content of ≤0.01%, making it suitable for rigid and flexible polyurethane foam systems requiring low residual solvent and controlled cell structure.
| HS Code | 527930 |
| Chemical Name | Methylene Chloride |
| Chemical Formula | CH2Cl2 |
| Cas Number | 75-09-2 |
| Molecular Weight | 84.93 g/mol |
| Boiling Point | 39.6 °C |
| Melting Point | -96.7 °C |
| Density | 1.326 g/cm3 at 25 °C |
| Vapor Pressure | 46.5 kPa at 20 °C |
| Solubility In Water | 1.3 g/100 mL at 20 °C |
| Flash Point | None (non-flammable liquid) |
| Autoignition Temperature | 556 °C |
| Ozone Depletion Potential | 0 |
| Global Warming Potential | 9 (100-year) |
| Physical State | Clear liquid |
| Color | Colorless |
| Odor | Ethereal, sweet odor |
| Blowing Agent Type | Physical blowing agent |
| Viscosity | 0.43 cP at 25 °C |
As an accredited Methylene Chloride Foam Blowing Agent factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | Methylene Chloride Foam Blowing Agent supplied in 200-liter sealed steel drums, ensuring safe storage, handling, and transport. |
| Container Loading (20′ FCL) | Loading 20′ FCL: secure drums/IBCs of Methylene Chloride foam blowing agent, with ventilation and proper segregation per dangerous goods regulations. |
| Shipping | Ship Methylene Chloride Foam Blowing Agent as UN1593, Dichloromethane, Class 6.1, PG III. Use sealed, corrosion-resistant drums or IBCs, securely braced. Ensure proper hazard labeling, placarding, and shipping papers. Avoid heat, ignition sources, and foodstuffs. Follow IMDG, IATA, and DOT regulations; ventilate and use PPE during loading. |
| Storage | Store methylene chloride foam blowing agent in a cool, dry, well-ventilated area away from direct sunlight, heat, and ignition sources. Keep containers tightly closed, upright, and clearly labeled, preferably in approved corrosion-resistant secondary containment. Avoid contact with strong oxidizers, acids, and moisture. Use explosion-proof ventilation and proper grounding; maintain spill containment and emergency eyewash nearby. |
| Shelf Life | Shelf life is typically two years when stored tightly sealed, cool, dry, and away from moisture and sunlight. |
On continuous slabstock lines running polyether polyol and toluene diisocyanate, methylene chloride is metered into the polyol blend after the day tank and before the low-pressure mixing head, functioning as a secondary physical blowing agent alongside the carbon dioxide generated by water–isocyanate reaction. The normal boiling point of 39.8°C places methylene chloride below the rising foam exotherm, so evaporation begins at the liquid pour front and continues through the early cure phase. The practical addition window in this production format is 3.0–12.0 pphp; below 3.0 pphp the density reduction is frequently lost within routine batch variation, while above 12.0 pphp the enthalpy demand of solvent evaporation suppresses the exothermic profile sufficiently to leave visible flow lines, hard seams, and cold spots in the bun. The worker-exposure control framework for this application is 29 CFR 1910.1052, with an 8-hour time-weighted average permissible exposure limit of 25 ppm and a 15-minute short-term exposure limit of 125 ppm; slabstock plants in the United States also operate under the applicable 40 CFR Part 63 NESHAP emission control requirements, which compel collection and routing of methylene chloride vapours from the foam tunnel, raw cure area, and cut-block storage. The downstream production process is a continuous trough pour: a travelling conveyor carries the liquid reaction mixture through a rise section under forced ventilation hoods, then into raw bun storage held under negative pressure for 24–72 h at ambient temperature, followed by horizontal and vertical cutting into rectangular blocks on a bandknife slitter. Representative low-pressure mixing heads on such lines deliver 40–250 kg/min, and the polyether polyol component viscosity at 25°C typically drops from a range of 1,800–3,600 mPa·s to 600–1,400 mPa·s after methylene chloride blending. Core density is measured under ISO 845:2006, compression load deflection under ISO 3386-1:2020, and fatigue performance under ASTM D3574-17; a methylene chloride level of 6 pphp commonly moves core density from approximately 28 kg/m³ to 21 kg/m³, although the exact delta depends on water content, tin catalyst concentration, and slabstock head pressure. Terminal finished product types include mattress foam cores, upholstery seating blanks, carpet underlay, and acoustical backing for laminated textile panels. The operational boundary is that methylene chloride must be substantially removed from the raw bun before skinning or flame lamination; residual blowing agent above the local emission threshold causes pinholes in subsequent adhesive lamination and can produce a visible solvent bloom on the cut surface.
Why Does Methylene Chloride Addition Destabilise Sink-Fill Uniformity in Cold-Cure Molded Seating Foam?
In high-resilience molded foam for automotive and motorcycle seating, methylene chloride is introduced at 2.0–6.0 pphp alongside water in the polyol component, but the effect is not a simple density reduction; the solvent redistributes the blowing load and modifies the timing of urea-phase separation that controls cell opening. At 6.0 pphp, the combination of methylene chloride evaporation and the exothermic reaction of modified MDI with polyether triol produces a lower demold density, commonly 38–52 kg/m³, yet sink-fill behaviour worsens: the skin surface collapses at thin cross-sections and vent locations because the liquid film at the mold wall is cooled below the gel threshold before the polymer network has sufficient modulus. The relevant automotive compliance standards are ISO 3795:1989 for horizontal flammability, VDA 278:2011-10 for volatile organic and semi-volatile organic desorption, and DIN 75201:2011-11 for gravimetric fogging; methylene chloride contribution to VOC mass is measured down to a reporting threshold of 10 µg/g toluene-equivalent response. The production process uses a high-pressure impingement mixing head, a metered pour into temperature-controlled steel molds at 50–65°C, and an in-mold dwell of 3–8 min before demolding; the demolded part is crushed through pinch rollers or a vacuum-crush station to open cell windows, then post-cured at 60–80°C for 2–4 h to strip residual methylene chloride. Published data for the exact relationship between methylene chloride addition and force-to-crush at thin sections is limited; operational limits are therefore set by mold fill weight and maximum internal cavity pressure rather than by a single prediction model. Terminal finished product types are automotive seat cushions, backrest bolsters, armrests, headrests, motorcycle saddle cores, and office seating cushions. The critical boundary is that adding methylene chloride above 6.0 pphp in this process tends to produce pinhole voids at the vent side, which are detectable as a loss of ISO 3386-1:2020 compression set uniformity across the part; therefore additions are only raised when the mold has a redesigned vent path and a higher clamping force.
When methylene chloride is metered at 1.5–8.0 pphp into MDI-based integral-skin formulations, the dominant process variable shifts from density reduction to the thickness and integrity of the non-cellular polyurethane skin that forms against the mold wall. Below 1.5 pphp, the density change is statistically indistinguishable from water-only control batches under routine production variance; above 8.0 pphp, solvent vapour escapes through the developing skin and creates surface defects that cannot be removed by post-molding trimming. The compliance profile for this downstream segment is governed by vehicle interior air-quality requirements rather than unprotected worker exposure alone: flammability is controlled by FMVSS 302 and ISO 3795:1989, while microcellular physical properties are tested under ASTM D3489-23, including density, tensile strength, and tear. The production process operates with a high-pressure or low-pressure mixhead pouring into machined aluminum molds held at 45–60°C, with an in-mold residence of 2–6 min; after demolding, the parts pass through a post-cure tunnel at 70–80°C for 60–180 min to strip residual methylene chloride below the applicable member state emissions limit. The formulation addition is normally 2–4 pphp when the target overall density lies between 300 kg/m³ and 600 kg/m³. Terminal finished product types are steering wheels, gearshift knobs, handbrake grips, door pull handles, armrest substrates, and motorcycle side panels. The incompatibility boundary is with formulations containing high amine levels or very fast gel catalysts: methylene chloride can be retained selectively in thick sections and later bloom to the surface, so additional curing time is required for parts thicker than 40 mm. Published data for the skin-density gradient in production tooling with methylene chloride concentrations above 5 pphp is limited; mold flow simulation generally underestimates the amount of skin rupture observed at sharp radii.
Methylene Chloride’s Narrow Processing Window in Polyester-MDI Microcellular Sole Elastomers
Methylene chloride’s benefit in polyester-MDI microcellular systems is the ability to reduce component viscosity and lower density without increasing water addition, but the processing window is narrow: the addition range is 0.5–4.0 pphp, while the accepted mold temperature band is only 40–55°C. At 0.5 pphp, the density reduction on a two-component sole casting line is typically less than 0.03 g/cm³; at 4.0 pphp, the skin of the outsole-facing surface begins to show pinholes because the gas phase nucleates before the prepolymer film closes. The applicable test standard for physical properties is ASTM D3489-23, and finished-article compliance is assessed under the general REACH substance restriction and Annex XVII framework; methylene chloride itself is not an SVHC, but its CLP classification as a category 2 carcinogen requires exposure minimisation during casting operations and local exhaust ventilation at the mixhead. The downstream production process uses a two-component high-pressure casting machine with a screw metering unit for the polyester polyol blend; the polyol component viscosity before methylene chloride addition is typically 1,500–3,500 mPa·s at 40°C, dropping to 800–1,500 mPa·s after addition, which improves flow into textured mold cavities. The mixed material is injected into hinged aluminum or steel molds preheated to 45–55°C; demold time is 4–8 min, followed by room-temperature curing for at least 24 h before trimming and adhesive bonding. Terminal finished product types include polyurethane midsoles, wedge soles, sandal footbeds, and orthotic inserts. The operational boundary is that methylene chloride is not retained in high-hardness clear-outsole systems because residual gas causes delamination at the adhesive interface; therefore its use is restricted to opaque microcellular midsoles where the surface will be abraded before cementing.
When Methylene Chloride Surpasses 10 pphp in Low-Density Lamination-Grade Foam, Solvent Condensation in the Post-Cure Oven Becomes the Controlling Limitation
At addition rates between 5.0 pphp and 12.0 pphp, methylene chloride serves the thin-sliced, low-density flexible foam segment as the primary physical blowing agent; the target core density on the slitter is commonly 12–18 kg/m³. The limiting control parameter is not the foam bun itself but the residual solvent load in the post-cure oven: when methylene chloride exceeds 10 pphp in low-density lamination-grade foam, the portion that bypasses extraction recondenses on duct surfaces held below 39.8°C, creating a fire-maintenance risk and increasing oven cleaning frequency. Published data for this specific configuration is limited, but the operational response is to reduce addition to 10 pphp or to raise oven exhaust temperature above the dew point of the solvent stream. Industry compliance for automotive acoustic parts uses ISO 10534-2:1998 for normal-incidence sound absorption coefficient, FMVSS 302 for horizontal burning rate, and VDA 278:2011-10 plus DIN 75201:2011-11 for desorption and fogging. Downstream production involves skiving the cured bun into sheets of 2–10 mm, adhesive-laminating or flame-laminating the foam to nonwoven scrims or decorative textiles, thermoforming the composite at 180–210°C, and die-cutting the finished contour. Terminal finished product types are automotive headliner substrates, hood silencers, dash insulators, under-carpet acoustic mats, and firewall absorption layers. The operational boundary is that residual methylene chloride in the foam must be below the emission threshold before flame lamination; otherwise the surface flame produces irregular burn-through and pinhole perforations at the bond line.
| Downstream segment | Compliance standard | Test designation or clause | Controlling value |
|---|---|---|---|
| Continuous flexible slabstock | Occupational exposure to methylene chloride | 29 CFR 1910.1052 | 25 ppm 8-h TWA, 125 ppm STEL |
| Cold-cure molded seating foam | Vehicle interior flammability | ISO 3795:1989 | Burn rate max 100 mm/min |
| Integral-skin interior components | Microcellular urethane physical properties | ASTM D3489-23 | Density 300–600 kg/m³ |
| Microcellular sole elastomers | Microcellular urethane physical properties | ASTM D3489-23 | Density reduction 0.03 g/cm³ at 0.5 pphp |
| Lamination-grade acoustic foam | Impedance tube sound absorption | ISO 10534-2:1998 | Normal-incidence absorption coefficient |
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- Methylene Chloride Foam Blowing Agent is manufactured under an ISO 9001 quality system and complies with relevant regulatory requirements.
- COA, SDS/MSDS, and related certificates are available upon request. For certificate requests or inquiries, contact: sales4@ascent-chem.com.
Technical-grade dichloromethane, CAS 75-09-2, is supplied for polyurethane foam production as a urethane-grade physical blowing agent with an assay of 99.9 wt% minimum and an amylene stabilizer package at 20–50 mg/kg. No single industry-wide model designation exists; vendor certificates typically identify the material as urethane-grade dichloromethane with amylene stabilization. The product is a clear, water-white liquid with a normal boiling point of 39.8–40.0°C, a density of 1.326 g/cm³ at 20°C, a vapour pressure of 47 kPa at 20°C, and a liquid viscosity of 0.43 mPa·s at 20°C. It functions as a latent physical blowing agent in flexible slabstock, viscoelastic, and selected molded polyurethane systems, where the foam exotherm converts the liquid to vapour and reduces apparent density without the urea formation associated with water. The commercial specification is normally verified by gas chromatography for assay, ASTM E203 for water content, ASTM D1613 for acidity, and ASTM D1353 for non-volatile residue. Typical acceptance limits include water 30 mg/kg maximum, acidity 5 mg/kg as HCl maximum, non-volatile residue 5 mg/kg maximum, and colour 10 Pt-Co maximum.
| Parameter | Acceptance range | Test method |
|---|---|---|
| Assay as dichloromethane | 99.9 wt% minimum | ASTM D4701 |
| Water content | 30 mg/kg maximum | ASTM E203 |
| Acidity as HCl | 5 mg/kg maximum | ASTM D1613 |
| Non-volatile residue | 5 mg/kg maximum | ASTM D1353 |
| Colour, Pt-Co scale | 10 maximum | ASTM D1209 |
| Stabilizer as amylene | 20–50 mg/kg | Vendor gas-chromatographic method |
As a physical blowing agent, dichloromethane is metered into the polyol stream before the mixhead on continuous slabstock lines. It reduces mix viscosity, lowers foam density, and softens load-bearing properties compared with water-blown foams of equivalent density. Unlike water, it does not consume isocyanate groups, so the formulation can maintain a lower isocyanate index while achieving comparable gas volume. This distinction has direct consequences for hardness, elongation, and compression set.
What Distinguishes DCM from Water, Hydrocarbon, and HFC Co-Blowing Agents in Flexible Slabstock?
Dichloromethane belongs to the physical blowing agent class, whereas water is a chemical blowing agent that liberates carbon dioxide through reaction with isocyanate. The most important operational consequence is that water creates polyurea segments that raise modulus and hardness, while dichloromethane contributes no urea and therefore softens the polymer. This difference is exploited when very low-density flexible foam must retain low indentation force deflection. DCM is therefore not a direct replacement for water; it is a co-blowing agent that adjusts the ratio of urea-derived load-bearing structure to free-rise gas volume.
Compared with cyclopentane and n-pentane, dichloromethane is not classified as a flammable liquid under ambient conditions, although it may form combustible vapour-air mixtures at elevated temperatures. This removes the explosion-prevention burden associated with hydrocarbon storage, but it introduces a higher toxicological burden because of the lower occupational exposure limits. Compared with HFC-245fa, dichloromethane has a much lower global warming potential but is a volatile organic compound and is generally unsuitable for closed-cell rigid insulating foams where the cell gas must remain in place and contribute to low thermal conductivity. Compared with methyl formate or acetone, dichloromethane has higher solvent strength and a boiling point above typical slabstock pouring temperatures, which can provide a smoother gas evolution profile but increases the risk of residual solvent retention in sealed foam packages.
| Blowing agent | Type | Normal boiling point | ODP | GWP, AR5 100-year | Flammability profile | Key limitation |
|---|---|---|---|---|---|---|
| Dichloromethane | Physical | 39.8–40.0°C | 0 | 9 | Not flammable liquid; combustible vapour possible at elevated temperature | VOC, occupational exposure limits, residual odour |
| Water / CO₂ | Chemical | CO₂ generated in situ | 0 | 1 | Non-flammable | Increases urea, hardness, and water-isocyanate exotherm |
| Cyclopentane | Physical | 49.3°C | 0 | <1 | Highly flammable liquid and vapour | Explosion-proof equipment required |
| HFC-245fa | Physical | 15.3°C | 0 | 858 | Non-flammable | F-gas regulation, GWP, cost |
| Methyl formate | Physical | 31.5°C | 0 | <1 | Highly flammable | VOC, reactivity with moisture, fast evaporation |
In flexible slabstock, water is the primary chemical blowing agent; dichloromethane is typically added at 3–8 parts per hundred polyol when density below 20 kg/m³ is required without excessive hardness. The isocyanate index is then adjusted downward to compensate for reduced urea, and physical property testing is performed in accordance with ISO 845 for apparent density and ISO 1798 for tensile strength. The selection between dichloromethane and hydrocarbons is therefore determined by the acceptable flammability classification of the plant, the available exhaust-abatement capacity, and the end-market specification for volatile emissions.
On continuous slabstock lines with high-pressure impingement mixheads operating at 10–20 MPa, dichloromethane is metered by magnetic or mass-flow pumps from a nitrogen-blanketed day tank held at 20–25°C. Because the liquid boils at 39.8°C, any stagnation in the metering circuit during a line stop can generate vapour lock; recirculation to the day tank and back-pressure valves set at 0.5–1.0 MPa are common. Published data for specific line configurations is limited, but process audits regularly identify insufficient cooling of the dichloromethane feed line as the dominant cause of density drift.
The endothermic vaporization of dichloromethane removes approximately 330 kJ/kg from the rising foam, reducing core temperature and minimizing scorch in low-density foams. However, excessively rapid vaporization when the mixhead temperature exceeds 30°C can produce internal blowholes, splits, or surface pinholes. The practical processing window is narrow; common practice is to keep dichloromethane below 8 php in open-celled slabstock foam because above this level closed-cell shrinkage may appear unless the cell-opening surfactant package is re-optimized. Because dichloromethane viscosity is 0.43 mPa·s, it reduces polyol blend viscosity; the exact magnitude depends on the base polyol molecular weight and filler loading. Changes of 0.5 php can produce measurable density shifts on continuous lines, though the absolute response is formulation-specific and published data for individual machine configurations remains limited.
Occupational Exposure Limits, Thermal Decomposition, and Ventilation Design
Dichloromethane is a hazardous volatile organic compound with strict occupational exposure ceilings. In the United States, 29 CFR 1910.1052 establishes an 8-hour time-weighted average permissible exposure limit of 25 ppm and a short-term exposure limit of 125 ppm, with an action level of 12.5 ppm. In the European Union, Directive (EU) 2017/164 sets a binding occupational exposure limit of 50 ppm (174 mg/m³) as an 8-hour time-weighted average and 100 ppm (348 mg/m³) as a short-term exposure limit. Local exhaust ventilation on slabstock lines must be designed to maintain time-weighted exposure below the lower of applicable limits; enclosure of the metering station and foam tunnel extraction are required.
Dichloromethane has an autoignition temperature reported at 556°C. Although it is not classified as a flammable liquid under ordinary ambient conditions, thermal decomposition in contact with open flames or hot surfaces can generate hydrogen chloride and trace phosgene. Welding on storage tanks must follow confined-space and hot-work procedures. Under REACH, Annex XVII entry 59 restricts the supply of paint strippers containing dichloromethane; industrial polyurethane foam production is subject to downstream user exposure-scenario obligations rather than that consumer restriction, but the same hazard classification drives ventilation and monitoring requirements.
When DCM Replaces HFC-141b in Integral-Skin and Rigid-Foam Applications
Dichloromethane is not a drop-in replacement for HFC-141b in closed-cell rigid polyurethane foam or insulating integral-skin parts. Its normal boiling point is above typical mould temperatures, and it does not provide the same low vapour thermal conductivity required for insulation values below 20 mW/m·K. For non-insulating semi-rigid molded seating and technical foam parts, dichloromethane has been evaluated as a density reducer where the closed-cell content can be managed by mechanical crushing or formulation adjustment. Published data for this specific configuration is limited, and the replacement requires separate optimization of mould venting because dichloromethane evolves more rapidly at demold temperatures than HFC-141b.
When dichloromethane replaces HFC-141b in any molded part, the blowing agent concentration must be re-optimized against part geometry and clamp force. The difference in vapour pressure at mould temperature affects the internal pressure profile during cure, and inadequate venting can generate surface porosity or part blowing. Equipment for molded polyurethane processing must therefore include enlarged vents and closed-loop temperature control on the mould surface. Unlike HFC-141b, dichloromethane contributes to workplace VOC mass balance and may require carbon adsorption abatement on the demould exhaust.
In viscoelastic and high-resilience slabstock formulations, dichloromethane is introduced into the polyol stream after the mixer for polyol, water, catalysts, and silicone surfactant but before the metering pump. The preblend temperature is maintained at 20–25°C to reduce vapour lock. Dichloromethane is often used at 3–6 php with water at 1.5–2.5 php. Because dichloromethane does not form urea, the hardness of a viscoelastic foam at a given density is lower than that of an all-water-blown counterpart; rebound resilience and compression set are evaluated using ASTM D3574 test methods. The limiting factor is not chemical compatibility—dichloromethane is generally stable in polyether polyols—but volatile organic compound mass balance and the potential for migration of residual solvent into PVC or ABS substrates when foam is packaged in closed containers. Storage of finished foam in sealed polyethylene film can increase residual dichloromethane concentration in the headspace; therefore forced-air post-curing or warehouse ventilation is required before packaging.
