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Ascent Petrochem Holdings Co., Limited

Klean Strip Methylene Chloride

    • Product Name: Klean Strip Methylene Chloride
    • Factroy Site: Binhai New Area, Tianjin, China
    • Price Inquiry: sales4@ascent-chem.com
    • Manufacturer: Ascent Petrochem Holdings Co., Limited
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    Specifications
    HS Code 662472
    Product Name Klean Strip Methylene Chloride
    Chemical Name Dichloromethane
    Chemical Formula CH2Cl2
    Cas Number 75-09-2
    Molecular Weight 84.93 g/mol
    Appearance Clear colorless liquid
    Odor Sweet chloroform-like odor
    Boiling Point 39.6°C (103.3°F)
    Melting Point -96.7°C (-142°F)
    Auto Ignition Temperature 556°C (1033°F)
    Vapor Pressure 47.4 kPa at 20°C (approximately 356 mmHg)
    Vapor Density 2.9 (Air = 1)
    Specific Gravity 1.33 at 20°C (Water = 1)
    Solubility In Water Slightly soluble (approximately 20 g/L at 25°C)
    Evaporation Rate Faster than n-butyl acetate (high volatility)

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

    Packing & Storage
    Packing Klean Strip Methylene Chloride comes in a sturdy metal can with a resealable lid, available in a 1-gallon quantity.
    Container Loading (20′ FCL) 20′ FCL container loading of Klean Strip Methylene Chloride: securely packed drums/pails, fully loaded, hazard-labeled, ventilated, and blocked for transit.
    Shipping Klean Strip Methylene Chloride ships as a hazardous material via ground transport only. It requires proper DOT labeling, UN1593 classification, and secure leak-proof packaging. Air freight is prohibited. Carriers must follow hazmat regulations, and recipients may need to verify local restrictions before delivery.
    Storage Store Klean Strip Methylene Chloride in its original, tightly sealed container in a cool, dry, well-ventilated area away from direct sunlight, heat, sparks, and open flames. Keep it separate from strong oxidizers, acids, and food items. Use secondary containment to catch spills, and ensure the storage area is inaccessible to children and pets.
    Shelf Life Shelf life is indefinite if stored tightly sealed, away from heat and moisture, in original container.
    Application of Klean Strip Methylene Chloride

    Technical-grade methylene chloride supplied under the Klean Strip specification is received at 99.9 wt% assay, ≤10 ppm water, and ≤5 ppm acidity as propionyl chloride equivalent. In industrial coating-removal systems, the solvent is let down to 70–85 wt% in a sealed low-shear mixer equipped with variable-frequency drive and jacket temperature control at 18–25 °C; the balance is a thickened organic phase containing 3–6 wt% methylcellulose or hydroxyethyl cellulose, 2–5 wt% paraffin wax, and 4–8 wt% mineral oil. The paraffin wax functions as an evaporation barrier, not as an adhesion promoter, and must not exceed 7 wt% because phase inversion produces a grainy film with reduced dwell-time performance on vertical aluminium fuselage skins. This industrial paint-stripping application is controlled under US EPA 40 CFR Part 63 Subpart GG for aerospace coating removal operations where methylene chloride-containing removers remain permitted under the 2024 TSCA methylene chloride risk management rule in 40 CFR Part 751 Subpart B, which requires a workplace chemical protection program, fume suppression, and recordkeeping. In the EU, REACH Regulation (EC) No 1907/2006 Annex XVII Entry 59 restricts the supply of paint strippers containing methylene chloride to industrial installations with trained personnel and controlled ventilation. Worker exposure is governed by OSHA 29 CFR 1910.1052, with an 8-hour TWA of 25 ppm, a STEL of 125 ppm, and an action level of 12.5 ppm, requiring air monitoring, medical surveillance, and respiratory protection during open-brush or airless spray application. Application on production lines uses airless spray tips of 0.015–0.025 in, depositing 1.5–2.2 L/m²; dwell time is held at 20–45 min at 20–27 °C, after which softened coating is removed with plastic scrapers or low-pressure water rinsing. Rinsate is decanted, and the methylene chloride content in water is stripped through closed-loop carbon adsorption before discharge. Terminal products include aircraft fuselage repainting cycles, railcar refurbishment, marine hull maintenance, and industrial machinery recoating, where high-speed removal of epoxy and polyurethane topcoats is specified.

    What Stabiliser Feed Rate Extends Non-Flammable Vapour Degreasing Bath Life Without Dropping Acid Acceptance?

    Maintaining a non-flammable vapour degreasing line for oxygen-service titanium alloy fittings requires a fresh methylene chloride feed rate that keeps acid acceptance above 0.15 g NaOH/100 mL and water content below 150 ppm. The stabiliser package is metered at 0.02–0.10 wt% based on daily solvent turnover; in open-top vapour degreasers, evaporation losses are typically 0.8–1.5 kg/h per 1 m² freeboard opening, and make-up solvent is added through a drowning-loop siphon to avoid stabiliser stratification. The degreaser operates at the methylene chloride boiling point of 39.6 °C, and parts are lowered into the vapour zone until condensation stops, indicating that part temperature has equilibrated with vapour temperature; total cycle time is 6–12 min with a final distillate spray of 1.5–2.0 L/min and drying of 2–5 min. Halogenated solvent cleaning lines are subject to US EPA NESHAP 40 CFR Part 63 Subpart T, which sets freeboard ratio, automated hoist, and idling cover requirements for batch vapour degreasers. ASTM D3698-04(2020) covers vapour degreasing solvent handling and solvent quality indicators, while worker exposure remains under OSHA 29 CFR 1910.1052. This downstream process is used for titanium and stainless steel components destined for passivation, anodising, or oxygen-cleaning before assembly; terminal product types include aircraft hydraulic valve bodies, titanium bone screw blanks, and high-purity gas manifold parts. The main process conflict is stabiliser depletion: when acid acceptance falls below 0.10 g NaOH/100 mL, liberated hydrochloric acid can initiate pitting on aluminium and titanium, so the bath is sampled every 8 h and the stabiliser-to-solvent ratio is adjusted before the next production shift.

    In solvent cementing of polycarbonate optical housings, a low-viscosity cement is compounded from 90–95 wt% methylene chloride and 5–10 wt% virgin polycarbonate resin dissolved under high-purity nitrogen at 25 °C to a Brookfield viscosity of 1,200–3,500 cP. The methylene chloride attack depth is controlled by solvent evaporation rate, which is a function of ambient dew point; above 22 °C dew point, moisture condensation creates surface blush and reduces lap-shear strength by as much as 20–35%, so production lines maintain dew point below 10 °C and relative humidity between 35% and 55%. Capillary-action application with 0.25–0.50 mm needle tips deposits 0.05–0.10 mL per linear joint; parts are fixtured at 1.5–2.5 bar clamping pressure for 60–120 s, then allowed to cure at 23 ± 2 °C for 24 h before mechanical testing. Bonded assemblies are tested per ASTM D638-14 Type V for tensile strength and per ISO 179-1:2023 for impact resistance; in medical device applications, ISO 10993-1:2018 and ISO 10993-18:2020 require chemical characterisation of residual methylene chloride in finished devices, with residual solvent in firm joints typically controlled below 25 ppm by headspace GC-MS. The addition ratio of methylene chloride is deliberately kept above 90 wt% because lower solvent content raises viscosity and prevents complete capillary wetting of close-fitting polycarbonate interfaces. Terminal products include polycarbonate instrument covers, acrylic display cases, fluid manifolds in optical readers, and solvent-bonded clear enclosures where adhesive bond lines would cause optical distortion.

    Neutral Alkaloid Extraction Requires pH Control, Countercurrent Wash Ratios, and Wiped-Film Distillation

    At pH 8.5–10.0, neutral freebase alkaloids partition from clarified fermentation broth into methylene chloride in a countercurrent mixer-settler battery of 3–5 stages operating at 20–25 °C; outside that pH window, ionised species remain in the aqueous raffinate and extraction efficiency falls below 85%. The solvent is metered at an aqueous-to-organic ratio of 1:1 to 3:1, and each stage residence time is 10–20 min, with conductivity probes monitoring the phase split so that the rag layer does not exceed 0.5 cm. The loaded organic phase contains 0.5–3.0 wt% crude alkaloid and is washed with 0.5 N sodium hydroxide at 5–10 vol% of the organic flow before concentration in a wiped-film evaporator at 40–50 °C and 80–120 mbar, recovering 95–98% of the methylene chloride for reuse. ICH Q3C(R9) classifies methylene chloride as a Class 2 residual solvent with a permitted daily exposure of 6.0 mg/day and a concentration limit of 600 ppm in finished drug product; USP <467> governs residual solvent testing by headspace gas chromatography, and EU GMP Part II for active pharmaceutical ingredients applies to solvent recovery and reuse. Extraction lines are designed to ATEX 2014/34/EU where co-solvents with flash points below process temperature are present, and methylene chloride itself is classified as non-flammable under standard closed-cup testing but must be kept below decomposition temperature in drying trains. The downstream process includes pH adjustment, carbon treatment, solvent drying over molecular sieves, and fractional distillation before re-entry into the extraction battery. Terminal product types include purified alkaloid intermediates for anticholinergic APIs, steroid intermediates, and quaternary ammonium precursors after downstream salt formation.

    When 2.5 Parts Auxiliary Blowing Agent Replaces 1 Part Water in Flexible Slabstock Polyurethane Foam

    When 2.5 parts per hundred polyol of methylene chloride is substituted for 1 part per hundred polyol of water in a 300 kg/min continuous flexible slabstock line, the CO₂ evolution from the isocyanate–water reaction is partly replaced by physical vaporisation of the auxiliary blowing agent, reducing foam core temperature from 155–165 °C to 132–145 °C and lowering nominal density from 28 kg/m³ to 19–22 kg/m³. The addition window is narrow: below 1.5 pphp density reduction is negligible, above 5.0 pphp the foam exhibits post-expansion collapse, debonding at the rise-profile side walls, and tensile tear values below 0.8 kPa as measured by ISO 1798:2019. The methylene chloride stream is metered through a mass-flow-controlled side injection port at 1.0–1.5 bar after the polyol blend has passed the main metering pump but before the mixhead, because pre-blending in the day tank raises vapour pressure above 0.7 bar and causes cavitation in the gear pump. Physical properties are tested per ISO 8307:2018 for resilience, ISO 3386-1:2021 for compression set, and ASTM D3574-17 for indentation force deflection; flammability performance is assessed per CAL TB 117-2013 or BS 5852 where required. Operator exposure is controlled under OSHA 29 CFR 1910.1052 because methylene chloride is released at the pour line and during the first 10 min of rise, with tunnel exhaust rates of 1,200–1,800 m³/h per metre of tunnel width needed to keep ambient concentrations below the action level of 12.5 ppm. The downstream production process includes continuous pouring onto moving paper, forced-air cooling, ambient cure for 24–72 h, and post-cure crushing to open cell windows. Terminal products include viscoelastic mattress cores, automotive seating underlay, and packaging cushioning where reduced density and increased softness are specified.

    Cellulose Triacetate Film Casting Solvent Ratios in Optically Isotropic Film Lines

    On a cellulose triacetate casting line, a 18–22 wt% polymer solution in a binary solvent of 90:10 w/w methylene chloride/methanol is fed to a slot die at 28–32 °C and 15–25 bar; the methylene chloride-rich phase evaporates first from the web surface, leaving a methanol-enriched boundary layer that suppresses surface skinning and improves optical flatness. The solvent ratio is not arbitrary: methanol below 6 wt% produces gel particles due incomplete polymer solvation, while methanol above 14 wt% increases solution viscosity above 18,000 cP and shifts the cloud point toward room temperature, causing die-line build-up and optical haze. Total solvent-to-polymer ratio is maintained between 3.5:1 and 4.5:1 w/w; recovered methylene chloride must have ≤0.1 wt% methanol and ≤50 ppm water before re-use in the dope mixer, and a purge stream prevents accumulation of non-volatile oligomers. Optical film is tested per ASTM D1003-21 for haze and luminous transmittance, per ISO 527-3:2018 for tensile properties, and per ISO 11455 for optical retardation; surface roughness is monitored by ASME B46.1. Workplace exposure is governed by OSHA 29 CFR 1910.1052 in the United States and by local implementation of Directive 98/24/EC in the EU, with cast line enclosures operated under negative pressure and solvent recovery by activated carbon adsorption. The downstream process includes melt-free casting onto polished stainless steel bands, multi-zone drying with solvent removal, film stretching, and final slitting. Terminal product types include liquid crystal display polarizer substrates, photographic film base, and protective optical films where high clarity and low birefringence are required.

    Supplied in bulk, 25 kg drums and 200 L steel drums. We provide import‑export service for global customers. Please contact us for latest price.

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    Certification & Compliance
    More Introduction

    Klean Strip Methylene Chloride is a professional-use, solvent-based coating remover supplied in 1-quart and 1-gallon metal containers. Distributor SKUs vary by region; the safety data sheet identifies dichloromethane (CAS 75-09-2) as the principal active solvent, with methanol and light petroleum distillates present as co-solvents or evaporation retarders. The product is formulated for cold stripping of alkyd, epoxy, polyurethane, latex, and lacquer films from ferrous and non-ferrous metal, hardwood, masonry, and concrete. Under 40 CFR 751.107, distribution for consumer paint and coating removal is no longer permitted in the United States; commercial use must be managed under a workplace chemical protection program and in accordance with OSHA 29 CFR 1910.1052.

    Why Evaporation Rate, Not Viscosity, Determines Open-Cell Cadence

    Dichloromethane has a normal boiling point of 39.8 °C, a liquid density of approximately 1.326 g/cm³ at 20 °C, and a vapor pressure of 47 kPa at 20 °C. Hansen solubility parameters for dichloromethane are reported as δD = 18.2 MPa0.5, δP = 6.3 MPa0.5, and δH = 6.1 MPa0.5; this positions the solvent within the solubility sphere of many alkyd binders and partially crosslinked epoxy-amine films. That solvency produces rapid film penetration, but the high evaporation rate shortens open-face working time and changes fleet-level material balance. Evaporation rate data under ASTM D3539-11 are reported by solvent suppliers as greater than 10 relative to n-butyl acetate at 1.0; exact formulation values depend on the paraffin wax or thixotropic retarder package. Flash point behavior is matrix-dependent: dichloromethane itself is classified as non-flammable under standard closed-cup testing, but the presence of methanol and petroleum distillate co-solvents can introduce a measurable closed-cup flash point. The lot-specific safety data sheet must be consulted before transfer into bulk process vessels.

    Incoming material is not treated as pure dichloromethane. Paraffin wax, thickeners, and co-solvents alter film appearance, evaporation barrier behavior, and low-temperature phase separation. Published lot-specific viscosity data are limited; incoming material should be checked by density measurement at 20 °C and by visual inspection for phase separation before large-scale immersion use. Because dichloromethane is listed as a hazardous air pollutant under Clean Air Act section 112(b), open-top tank operation requires emission controls that are not required for slower-evaporating dibasic ester or benzyl alcohol systems.

    Brush-applied work on millwork typically proceeds by saturating 0.4–0.8 m²/L at 18–25 °C. The wet film remains under a thin evaporation-retarder layer for 10–30 min. Lifting is completed with a plastic scraper; residues are neutralized according to the product data sheet and the surface is dried before recoating. Completion of coating removal may be evaluated using ASTM D3359-17 Method A, with a rating of 5A indicating no visible coating residue after crosscut tape pull. Published dwell-time data for this specific packaged formulation are limited; plant trials on multi-layer alkyd enamel over hardwood show that reapplication may be required when total film thickness exceeds 250 µm.

    What Changes When Immersion Cells Replace Brush Application on Hardware Lines?

    On controlled production lines, mild steel and brass hardware are immersed in open-top cells maintained at 20–24 °C. Liquid level and density are checked each shift because evaporative loss of dichloromethane increases resin concentration and slows coating penetration. Local exhaust is configured to achieve a capture velocity of 0.5–1.0 m/s across the tank perimeter, as recommended in the ACGIH Industrial Ventilation manual. Diffusion rate into crosslinked coatings is temperature-dependent; heating above 27 °C is not typical without sealed vapor containment and continuous monitoring. Photoionization detectors may under-respond to dichloromethane; workplace monitoring is more reliably performed by NIOSH Method 1005, which uses solid sorbent collection followed by gas chromatography. Without adequate border exhaust, the combination of vapor pressure and open liquid surface area can produce concentrations above the OSHA action level of 12.5 ppm as an 8-hour time-weighted average.

    Solvent Performance Markers Across Four Coating Removal Chemistries

    The primary separation from N-methyl-2-pyrrolidone, dibasic ester blends, and benzyl alcohol is in evaporation rate and solvency toward cured epoxy-amine and two-component polyurethane films. NMP shows lower vapor pressure but slower diffusion into highly crosslinked clearcoats. Dibasic ester formulations are useful in low-odor stripping but frequently fail to swell fully cured epoxy under 30-minute dwell. Benzyl alcohol leaves a persistent oily film that requires alkaline detergent rinsing. Methylene chloride-containing formulations remove crosslinked coatings more aggressively, but require stricter exposure controls and cannot be used on many engineering plastics.

    Comparative solvent properties used in cold coating removal
    Parameter Dichloromethane NMP Benzyl alcohol Dibasic ester blend
    Normal boiling point (°C) 39.8 202 205 196–225
    Vapor pressure at 20 °C, approximate (kPa) 47 0.03 0.01 0.03
    Relative evaporation rate, n-butyl acetate = 1.0 >10 0.03 0.01 0.01
    Typical failure mode on cured epoxy Rapid swelling and lifting Slow penetration; long dwell Incomplete lift; oily residue Poor softening under short dwell
    Primary process constraint Vapor control Residual solvent retention Residue removal High boiling residue

    Use of a methylene chloride product is not interchangeable with slower solvents in immersion cells because the mass balance of the tank is dominated by evaporative loss. Replenishment schedules must be adjusted to measured density and not simply to volume. A drop in density may indicate selective loss of dichloromethane; a rise in viscosity may indicate accumulation of stripped resin. Both conditions reduce stripping rate and may create a sticky boundary layer at the solvent-coating interface.

    If Ambient Temperature Exceeds 25 °C, Enclosure Vapour Controls Must Be Altered

    Above 25 °C, open-face application can create localized vapor accumulation near the workpiece surface. Process enclosures should be operated with negative pressure, and air discharge must be routed to filtration or abatement if the facility emission inventory requires it. The product is not to be heated by open flame, strip heaters, or unjacketed vessel walls; decomposition or hot-surface contact can generate hydrogen chloride and phosgene. Use of compressed air to dry stripped surfaces is discouraged unless the compressed air is filtered and the area is equipped with point extraction.

    U.S. workplace exposure thresholds for dichloromethane
    Limit or benchmark Value Regulatory or reference source
    8-hour permissible exposure limit 25 ppm OSHA 29 CFR 1910.1052
    Action level 12.5 ppm OSHA 29 CFR 1910.1052
    15-minute short-term exposure limit 125 ppm OSHA 29 CFR 1910.1052
    ACGIH TLV-TWA 50 ppm ACGIH threshold limit values
    NIOSH immediately dangerous to life or health 2300 ppm NIOSH Pocket Guide

    On concrete floors, the product is applied by low-pressure flow coat or squeegee. The first application is maintained as a continuous film for 10 min; a second application is applied when the film begins to dry or when the coating remains firmly attached. Polyethylene sheeting is used only where local exhaust can be maintained, because covering increases vapor residence time at the surface. The use of methylene chloride on porous concrete can carry dissolved coating residue into the substrate; after stripping, the surface is neutralized and checked for residual solvent before application of a new coating system. Published extraction data for this specific product configuration are limited, and field trial panels are recommended before full-scale use.

    Operating Limitations and Substrate Incompatibility Boundaries

    The product is incompatible with polycarbonate, acrylic, ABS, and many vinyl-based solid surfaces. It can stress-crack or dissolve these substrates during contact. It should not be applied near strong oxidizers, strong alkalis, or active metals. Closed containers contaminated with caustic or amine-based paint removers may pressurize and should not be mixed without venting. The product is intended for professional use only; commercial operators must maintain the workplace chemical protection program specified in 40 CFR 751.107, including exposure monitoring, medical surveillance, and hazard communication. Transfer from bulk containers to point-of-use cells should occur in a closed or mechanically ventilated area, and spent stripper waste must be managed under RCRA hazardous waste determination procedures. Product performance is best characterized on production-scale coupons rather than small panels, because ventilation, batch age, and solvent depletion dominate integrated removal rate more than the concentration of the active solvent alone.