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Poly(oxymethylene) Dimethyl Ethers

    • Product Name: Poly(oxymethylene) Dimethyl Ethers
    • Factroy Site: Yudu County, Ganzhou, Jiangxi, China
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    • Manufacturer: Ascent Petrochem Holdings Co., Limited
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    Specifications
    HS Code 826627
    Chemical Name Poly(oxymethylene) dimethyl ethers
    Cas Number 13352-75-5
    Molecular Formula CH3O(CH2O)nCH3, where n = 3 to 5 for typical product
    Molecular Weight 136 to 196 g/mol (depending on n)
    Density 1.00 to 1.10 g/cm3 at 20°C
    Boiling Point Approximately 200 to 280°C for n = 3 to 5
    Melting Point Approximately -40 to -10°C for n = 3 to 5
    Flash Point 60 to 100°C (typical)
    Cetane Number 60 to 90
    Oxygen Content 47 to 49 wt% for n = 3 to 5
    Viscosity 1.0 to 2.5 mPa·s at 25°C
    Solubility Miscible with diesel and hydrocarbons; limited water solubility

    As an accredited Poly(oxymethylene) Dimethyl Ethers factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing Poly(oxymethylene) dimethyl ethers are packaged in 200 L steel drums, 1,000 L IBC totes, or bulk tankers.
    Container Loading (20′ FCL) 20′ FCL loading of Poly(oxymethylene) Dimethyl Ethers: secure drums/IBCs, avoid moisture, ventilate, and ensure chemical compatibility.
    Shipping Poly(oxymethylene) dimethyl ethers ship as stable, low-volatility liquids in sealed drums, IBCs, or stainless-steel tankers. Protect from moisture and incompatible oxidizers, and store in cool, ventilated areas away from ignition sources. No special hazardous classification generally applies; use standard chemical handling, labeling, and spill-containment procedures.
    Storage Store poly(oxymethylene) dimethyl ethers in a cool, dry, well-ventilated area away from heat, ignition sources, and oxidizing agents. Use tightly sealed containers made of compatible materials, such as stainless steel or HDPE. Prevent moisture ingress and contamination. Ground containers to avoid static buildup, label clearly, and inspect regularly for leaks or damage.
    Shelf Life Shelf life is typically 12 months when stored tightly sealed in a cool, dry place away from moisture and heat.
    Application of Poly(oxymethylene) Dimethyl Ethers

    The diffusion-flame soot formation mechanism in heavy-duty direct-injection diesel engines responds to oxygenated blendstocks whose molecular backbone contains C–O–C linkages rather than C–C chains. Poly(oxymethylene) dimethyl ethers with nominal chain length n=3–5 and the general structure CH3O(CH2O)nCH3 carry oxygen at 47–49 wt%, which reduces local equivalence-ratio peaks and suppresses acetylene-based soot precursor growth during the premixed-to-diffusive transition. Commercial PODE n=3–5 blendstock is specified at 1.05–1.06 g/cm³ density and 1.1–1.5 mm²/s kinematic viscosity at 40°C, creating a direct constraint under EN 590:2022, Table 1, where density must remain between 820 kg/m³ and 845 kg/m³. For a paraffinic base diesel at 830 kg/m³, the density ceiling permits approximately 6.5 vol% PODE n=3–5; for a lower-density base at 820 kg/m³, the ceiling permits approximately 10.4 vol%. Engine and emissions trials frequently use 10–20 vol% additions to isolate particulate suppression effects, but those trial fuels sit outside the density envelope of EN 590:2022 unless the base fuel is reformulated. The final highway diesel must also meet ASTM D93 flash point above 55°C, ASTM D445 viscosity of 2.00–4.50 mm²/s, and ASTM D613 cetane number of at least 51.0, while the oxygenated blendstock raises derived cetane number and reduces particulate mass in constant-speed engine tests.

    Blending at a terminal is executed through a side-stream proportioning pump with 316L stainless steel wetted parts, discharging into a static mixer upstream of the final diesel rack. Coriolis mass flow meters with ±0.2% accuracy and near-infrared oxygenate analysers sequence the PODE injection to avoid batch rejection on density, while the PODE storage vessel is nitrogen-blanketed because atmospheric moisture uptake above 200 mg/kg shifts water separation behaviour in coalescer filters. The low kinematic viscosity of the blendstock reduces boundary lubrication film thickness, so the finished product is frequently additised with lubricity improver and verified by ASTM D6079 high-frequency reciprocating rig wear scar limits. Common-rail heavy-duty engines operated on density-compliant blends exhibit lower smoke opacity at rated torque, but fleet fuel managers must re-tune water separators and monitor elastomer compatibility in fuel-pump seals where n=3-rich cuts can alter swell characteristics relative to hydrocarbon-only diesel. Terminal products include EN 590 B7 highway diesel for Euro VI and China VI truck fleets, municipal bus depots, and standby generator sets where particulate and soot control in transient load acceptance is operationally critical.

    PODE n=3–5 volume fractionCalculated density at 15°C, base 820 kg/m³Calculated density at 15°C, base 830 kg/m³
    0 vol%820.0 kg/m³830.0 kg/m³
    5 vol%832.0 kg/m³841.5 kg/m³
    7 vol%836.8 kg/m³846.1 kg/m³
    10 vol%844.0 kg/m³853.0 kg/m³

    What Limits ISO 8217 Distillate Marine Fuel Blends Containing PODE n=3–5?

    Marine distillate fuel blending differs from on-road diesel because the statutory flash point is controlled by SOLAS II-2, Regulation 4.2.1 at 60.0°C minimum, not the 55°C applied to highway diesel. PODE n=3-rich streams with flash points near 55°C can pull an otherwise compliant DMA or DMZ blend below the maritime threshold, shifting blend specifications toward n=4–5-rich cuts whose higher boiling fractions maintain the required closed-cup value under ASTM D93 Procedure B. The derived cetane number of PODE n=3–5 is high, but ISO 4264 calculated cetane index does not account for oxygenate ignition behaviour; therefore marine fuel suppliers measure ignition quality by ASTM D7668 derived cetane number when PODE content exceeds 5 vol%. Sulphur compliance under MARPOL Annex VI, Regulation 14.1.3 is not adversely affected because PODE n=3–5 carries negligible sulphur, allowing the resulting marine gas oil to remain below the 0.10 wt% emission control area limit. The practical addition window is 5–15 vol% in ISO 8217 DMA/DMZ formulations, with the upper bound governed by flash point, density, and the altered water separation behaviour in marine fuel service tanks.

    Bunker barge operations meter PODE n=4–5-rich blendstock into the distillate line after the custody transfer meter, then pass the blended stream through a static mixer and a sampling manifold aligned with ISO 13739 bunkering procedures. The oxygenated blendstock reduces interfacial tension between free water and fuel, which requires lower flow velocity through onboard coalescer filters and may increase water carryover if unpurified fuel is transferred directly to day tanks. Centrifugal purifiers with gravity disc settings optimised for distillate fuels must be re-set because PODE blends show different neutral plane behaviour; shipboard engineers have observed that water removal efficiency can drop when the n=4–5 content exceeds 12 vol% unless the purifier throughput is reduced by approximately 15–20%. The terminal product is ISO 8217 DMA or DMZ marine gas oil intended for harbour craft, inland waterway vessels, and auxiliary engines operating inside sulphur emission control areas where particulate and black-carbon reduction at low engine loads supports port air quality requirements.

    Metal-finishing lines that formerly operated trichloroethylene or n-propyl bromide under halogenated solvent degreasing regulations have evaluated PODE n=2–4 blends for immersion and ultrasonic cleaning because the ether-ester backbone dissolves high-molecular-weight drawing oils, waxes, and rosin-based fluxes without introducing chlorinated solvent residues. A formulated degreaser containing 20–50 wt% PODE n=2–4 is balanced with branched aliphatic hydrocarbons and glycol ethers to maintain a closed-cup flash point above 35°C, while the n=2-rich portion of the mixture lowers surface tension and penetrates close-tolerance part geometries. Regulatory positioning avoids the halogenated solvent degreasing controls of U.S. EPA 40 CFR Part 63 Subpart T and the restriction routes of EU REACH Annex XVII, although the n=2 fraction with a flash point near 32°C requires explosion-proof equipment under ATEX Directive 2014/34/EU when solvent is heated above ambient. The solvent is applied in multi-stage immersion lines at 40–65°C, followed by ultrasonic agitation at 40–60 kHz and vacuum degreasing; solvent recovery is carried out by wiped-film evaporation at 80–150°C under reduced pressure to limit thermal cleavage of the acetal linkages. Terminal products include pH-neutral industrial degreasers for aluminium, copper, and carbon steel, optical component cleaners, and pre-paint wiping solvents where evaporative residue must remain below 5 mg/m².

    Non-Chlorinated Paint Stripper Gel Chemistry Based on PODE n=2–4 and Acid-Activator Package

    Reformulation of architectural and aerospace maintenance strippers away from dichloromethane is driven by EU REACH Annex XVII, Entry 59, which restricts dichloromethane in paint removers; PODE n=2–4 provides a dipolar aprotic-like solvation shell that swells crosslinked epoxy, polyurethane, and alkyd films without the hydrogen-bonding volatility of chlorinated methanes. A thickened stripper comprises 30–60 wt% PODE n=2–4, 10–20 wt% aromatic co-solvent, 2–5 wt% acid activator such as p-toluenesulphonic acid or formic acid, 3–8 wt% cellulosic or fumed-silica thickener, and 2–5 wt% surfactant to stabilise the gel film. The acid activator catalyses cleavage of ester and urethane crosslink sites at room temperature, while the PODE fraction retards solvent flash-off from the gel surface and extends dwell time on vertical steel and aluminium substrates. Formulations are checked for flash point under EN ISO 2719 or ASTM D93, and the thickened system must retain a sag-resistant film without phase separation after 72 h storage at 50°C.

    Production of the stripper is conducted in a high-shear disperser at 800–1500 rpm with acid addition sequenced after thickener hydration to prevent lumping; the batch is then vacuum-deaerated to remove entrapped air that would create pinholing in the applied gel. The product is applied by airless spray at 100–150 bar or by brush and trowel for vertical masonry and steel structures, with dwell times between 4 h and 12 h depending on coating age and crosslink density. Removal is completed with water jetting at 100–150 bar or mechanical scraping, after which the substrate is rinsed and tested for residual coating adhesion by ASTM D3359 crosshatch adhesion. Terminal product types include civil maintenance paint strippers for bridges and process plant, graffiti removal pastes, and aircraft MRO coating removers where substrate corrosion limits require non-halogenated chemistry and long gel hold times on riveted aluminium skins.

    When EU Stage V Non-Road Mobile Machinery Fuels Demand Soot Abatement Without Urea Aftertreatment

    Non-road mobile machinery engines covered by Regulation (EU) 2016/1628, Annex II are frequently calibrated without selective catalytic reduction because of machine space constraints and cost, shifting greater particulate control burden onto in-cylinder fuel chemistry. PODE n=3–5 addition at 5–12 vol% to off-road diesel lowers particulate matter and smoke opacity at high-load, low-speed operating points typical of excavators, wheel loaders, and agricultural tractors; the addition window is narrower than on-road diesel because off-road fuel specifications in some member states permit density above 845 kg/m³ but still require flash point and cold-flow protection. The oxygenated blendstock alters the injection event by reducing fuel viscosity and increasing lubricity additive demand, which must be compensated in the final fuel. Published data for NRMM duty cycles with PODE blends are more limited than for on-road heavy-duty cycle tests, so emissions benefit transfer from WHTC and ESC data to real-world construction machine duty cycles should be treated as directional rather than exact.

    Mobile fuel bowsers for construction sites dose PODE n=3–5 through a split-stream proportioning unit after the primary filtration stage, followed by a 2 µm absolute barrier filter because the blendstock can mobilise tank sludge and destabilise asphaltenes in poorly maintained off-road diesel storage tanks. The high-pressure common-rail pump operates at 180–250 MPa in Stage V engines; PODE blends with lower viscosity than conventional diesel shift the leakage and volumetric efficiency characteristics of the pump, so engine manufacturers restrict continuous PODE content in warranty documentation. The terminal product is a Stage V off-road diesel for construction machinery, agricultural tractors, and stationary generator sets where particulate emissions during load acceptance and the absence of urea aftertreatment infrastructure make fuel-borne oxygen a practical soot-control measure.

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    Certification & Compliance
    More Introduction

    Poly(oxymethylene) dimethyl ethers, designated PODE or OME depending on regional nomenclature, are a homologous series of methyl-terminated oxymethylene oligomers described by CH3O(CH2O)nCH3, where n is the number of incorporated formaldehyde units. The commercial diesel-relevant model interval is n=3 through n=5, frequently labelled OME3–5 or PODE3–5; the product is a clear liquid, not a high-molecular-weight polyoxymethylene engineering resin. A representative distribution may contain 35–50 wt% OME3, 40–55 wt% OME4, and 5–15 wt% OME5, with OME2 capped below 2 wt% to maintain flash point. Because the molecule contains no carbon–carbon bonds, the oxygen mass fraction in the n=3 to n=5 interval ranges from 47.0 wt% to 48.9 wt%. This structural feature directly influences ignition behaviour, solvency, density, and hydrolysis sensitivity.

    Industrial product designations are oligomer-window models rather than isolated single-molecule grades. A PODE3–5 grade is specified as a distribution; a PODE4-enriched grade may be produced by distillation or selective synthesis for higher flash-point applications, while a PODE2-rich grade is sold into solvent and cleaning duties where lower viscosity and higher volatility are desired. The chemical identity remains the same, but the safety and performance envelope shifts with chain length.

    What Limits the Diesel-Blending Homologue Window from n=3 to n=5?

    The volatility and low-temperature boundaries are set by chain length. OME1, commonly called methylal, has an atmospheric boiling point near 42°C and a flash point near -18°C, which is outside diesel fuel blending safety limits under ASTM D975 and EN 590. OME2 remains too volatile and its flash point is below 40°C, although it is lower in viscosity and can function as a solvent. At n=6 and above, atmospheric boiling point rises beyond 280°C; published data for isolated homologues above n=5 remain limited, and distillate recovery under ASTM D86 deteriorates. OME3, OME4, and OME5 provide a boiling interval that approximates the heavy middle distillate range, reported near 156°C, 202°C, and 242°C respectively. The n=3 to n=5 mixture typically yields a flash point above 60°C by ASTM D93 and a boiling range of 150–245°C by ASTM D86.

    A production bottleneck arises in the isolation of high-purity OME5. Because the acetal linkages are acid-sensitive, atmospheric or low-vacuum distillation must avoid prolonged bulk temperatures above roughly 160°C. If reboiler residence time is excessive, acid-catalysed transacetalization shifts the distribution toward OME2 and OME3, reducing isolated OME5 yield and broadening the final specification. Batch-to-batch variance in n=5 content is therefore more sensitive to distillation-column pressure drop and reboiler fouling than to feedstock stoichiometry alone.

    Certificates of analysis for a diesel-grade OME3–5 are built around chain distribution, water content, total acidity, density, viscosity, boiling range, and flash point. No harmonized ASTM specification currently defines OME3–5 as a finished fuel; the values below are typical producer specification ranges and are verified using fuel and chemical test methods. Chain distribution is usually determined by gas chromatography with flame ionization detection because the homologous response factors differ from aromatic hydrocarbon calibrations. Water content is a release-critical parameter: water accelerates hydrolysis of acetal linkages to formaldehyde and methanol, and the resulting formaldehyde can oxidize to formic acid. Acidity is therefore controlled at the parts-per-million level to protect common-rail injector internals from electrochemical corrosion.

    Typical commercial specification framework for OME3–5 diesel-grade poly(oxymethylene) dimethyl ethers
    PropertyTypical limit or rangeTest method
    Elemental oxygen47.0–48.5 wt%ASTM D5291 / combustion analysis
    n=3 content35–50 wt%GC-FID, internal method
    n=4 content40–55 wt%GC-FID, internal method
    n=5 content5–15 wt%GC-FID, internal method
    n=2 content≤2 wt%GC-FID, internal method
    Water≤300 mg/kgISO 12937
    Total acid number≤0.10 mg KOH/gASTM D664
    Density at 20°C1.03–1.08 g/cm³ISO 12185 / ASTM D4052
    Kinematic viscosity at 40°C0.9–1.4 mm²/sISO 3104
    Flash point, PMCC≥60°CASTM D93
    Boiling range150–245°CASTM D86

    The flash point, density, and boiling range should be measured on each batch after any water removal or neutralization step. A finished batch with ≥60°C PMCC flash point and ≤2 wt% OME2 is considered suitable for diesel pool blending; a solvent-grade PODE2-rich product may intentionally fail this flash-point criterion while meeting a lower-viscosity specification.

    Physicochemical Limits, Boiling Behaviour, and Oxygen Mass Fraction

    Density at 20°C is significantly higher than hydrocarbon diesel. A mixed OME3–5 batch typically measures 1.03–1.08 g/cm³ under ISO 12185, compared with 0.820–0.845 g/cm³ for an EN 590 diesel. Kinematic viscosity at 40°C sits in the 0.9–1.4 mm²/s range by ISO 3104, below the 2.0 mm²/s minimum in EN 590. The low viscosity creates a measurable lubricity loss: neat OME3–5 in a high-frequency reciprocating rig under ISO 12156-1 normally exceeds the 460 µm wear-scar limit unless a lubricity improver is added. Common-rail pumps with fuel-lubricated plungers and control valves are particularly sensitive to this property at rail pressures above 200 MPa.

    Oxygen mass fraction changes with n. OME3 carries approximately 47.0 wt% oxygen, OME4 48.1 wt%, and OME5 48.9 wt%. This is almost four times the oxygen content of a typical FAME biodiesel and 1.35–1.40 times that of ethanol. The absence of carbon–carbon bonds suppresses soot nucleation from the fuel structure; engine-out particulate reduction is reported in the 30–50% range in published compression-ignition studies at high exhaust gas recirculation, but the exact reduction depends on injection timing, piston bowl geometry, and lubricant-derived ash. The boiling range must be read as a homolog distribution, not a single-component phase-change point. If fractional distillation is poorly controlled, carryover of OME2 below 150°C lowers flash point, while OME6 formation raises viscosity and risks cold-filter plugging.

    The material displays Newtonian behaviour across ordinary shear rates; shear-thinning is not observed in production-scale storage. Cold-flow data are less standardized than hydrocarbon diesel, but n=5 crystallization is the limiting factor at low temperature. Published data for isolated OME5 cloud point is limited, so cold-filter plugging tests should be performed on the finished blend rather than inferred from diesel pour point.

    In heavy-duty high-pressure common-rail engines, OME3–5 is blended at 5–15 vol% into ultra-low-sulfur diesel to reduce filter smoke number and particulate mass without requiring a DME-type pressurized fuel tank. The high cetane number shortens ignition delay and lowers premixed combustion fraction, while the oxygen storage capacity reduces local equivalence ratio in the fuel-rich spray core. Engine studies report soot reductions of 30–50% at high exhaust gas recirculation settings, but the magnitude cannot be generalized beyond the specific engine calibration. The lower net calorific value of 20–21 MJ/kg, compared with 42.8–43.1 MJ/kg for mineral diesel, requires delivery maps to be recalibrated if brake mean effective pressure is to be preserved. Fuel mass flow through the high-pressure pump increases for a fixed acceleration load because density compensation is only partial.

    Solvent use is concentrated in high-flash degreasing, resin cleanup, and polar co-solvent formulations where the specification forbids aromatic hydrocarbons. The product's polarity is stronger than hydrocarbon solvents but lower than water-miscible ether-alcohols such as glycol diethers. It swells epoxy and polyester resins in cured or uncured states and can extract sebacate plasticizers from nitrile rubber. Vapour degreasing with this material is not a direct replacement for stabilized chlorinated solvents because the boiling range is too high and the stabilizer chemistry differs; published data for vapour-degreasing configurations is limited.

    When PODE Contacts Fuel-Carrying Elastomers and Metallic Components

    Material compatibility is governed by the polar acetal structure. Standard nitrile rubber compounds with ester plasticizers show volume loss and hardening after static immersion in neat OME3–5; seals must be evaluated under ISO 1817 at the intended blend concentration and temperature. Peroxide-cured hydrogenated nitrile and high-fluorine FKM elastomers are candidate seal materials, but no single fluoroelastomer is universally acceptable. Polyamide 11 and polyamide 12 fuel lines are less prone to swelling than plasticized PVC or polyurethane. The low viscosity of OME3–5 also reduces hydrodynamic film thickness in sliding injector components, so elastomer compatibility and lubricity must be validated together.

    For metals, zinc, copper, and brass should be excluded from long-term service because transition-metal ions accelerate peroxide formation and acid development. Stainless steel grades 304L and 316L, or high-density polyethylene, are preferred for storage and transfer. Carbon steel may be used only with continuous water removal and filtration below 200 mg/kg water; otherwise iron-catalysed peroxide formation creates low levels of formic acid and oligomeric solids. When the product is exposed to humid air, hydrolysis can generate formaldehyde and methanol. Vent dryers or nitrogen padding are therefore applied to fixed-roof tanks with weak acid scavengers in the vapour space.

    A Comparative Profile Against Dimethyl Ether, Methylal, and Mineral Diesel

    The product occupies the space between compressed gaseous DME and highly volatile methylal. Dimethyl ether has 34.8 wt% oxygen and a boiling point near -25°C, so it requires pressure vessels and dedicated injection hardware. Methylal has 42.1 wt% oxygen but an atmospheric boiling point near 42°C, making it unsuitable as a main diesel pool component. Ethanol has 34.7 wt% oxygen and introduces water miscibility, distillation-curve disruption, and pump cavitation in blends unless the base diesel is reformulated. FAME biodiesel has a suitable boiling range but oxygen is limited to 10.8–11.5 wt%, and unsaturated ester chains undergo autoxidation. OME3–5 combines a diesel-compatible boiling range with 47–49 wt% oxygen and a flash point high enough for conventional liquid-fuel handling, but the material requires addition of lubricity and hydrolysis inhibitors. The comparative values are summarised in Table 2.

    Representative literature values for OME3–5 and reference oxygenates; product certificates and fuel standards remain controlling.
    PropertyOME3–5EthanolDimethyl etherMethylal (OME1)EN 590 dieselFAME biodiesel
    Oxygen content (wt%)47.0–48.934.734.842.10 (hydrocarbon baseline)10.8–11.5
    Density at 20°C (g/cm³)1.03–1.080.7890.67 (liquid under pressure)0.860.820–0.8450.880–0.900
    Boiling point or range (°C)150–24578-2542170–360320–360
    Flash point, PMCC (°C)≥6013-41-18≥55≥101
    Cetane number70–90 (reported, n-dependent)8–1155–6028–35≥51≥51

    Bulk storage of OME3–5 is normally maintained in fixed-roof or floating-roof tanks fitted with nitrogen blanketing or desiccant dryers. Water ingress is controlled below 300 mg/kg through closed-loop unloading and hydrophobic tank vents. Side-side mixers or recirculation loops prevent stratification between n=3-rich and n=5-rich layers after prolonged idle periods. Sampling practices should avoid repeated atmospheric exposure because acetal hydrolysis increases with dissolved water and temperature. Downstream of storage, the product is prefiltered through 2 µm absolute media before entering high-pressure common-rail test benches; hydrolysis residues and particulate can deposit on high-pressure relief valves and fuel metering orifices. Batch-to-batch pH and water checks are performed after any caustic or weak-base neutralization step in production, and the neutralized material is stabilised with an antioxidant that does not contribute metallic ash.

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