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Methanol

Methanol, also known as methyl or wood , is the simplest aliphatic and an with the CH₃OH and a molecular weight of 32.04 g/mol. It appears as a colorless, volatile, that is completely miscible with and has a faintly sweet, pungent odor similar to ethyl . Methanol is highly toxic upon , , or skin , primarily due to its metabolism into and , which cause , optic nerve damage, and potential developmental toxicity. Globally, methanol is one of the most widely produced and utilized chemicals, with annual production exceeding 100 million metric tons, primarily through the of to produce synthesis gas (), followed by catalytic . Approximately 70% of methanol is employed as a feedstock in , yielding key products such as , acetic acid, methyl tert-butyl ether (MTBE) for additives, and for fuels and refrigerants. The remainder serves as an industrial solvent, agent in windshield washer fluids, and a blend component in fuels for vehicles and power generation, including emerging applications in renewable methanol production from or CO₂ to support transitions. Despite its versatility, methanol's flammability requires careful handling with dry chemical, CO₂, or alcohol-resistant foam extinguishers, and its toxicity necessitates strict regulatory controls in occupational and environmental settings.

Properties

Physical properties

Methanol, with the molecular formula CH₃OH, is the simplest , featuring a (CH₃-) covalently bonded to a hydroxyl group (-OH). Its is 32.042 g/mol. At standard conditions, methanol appears as a colorless, volatile liquid possessing a mild alcoholic . Key thermodynamic properties include a of −97.6 °C and a of 64.7 °C at standard . The is 0.7918 g/cm³ at 20 °C, and the is 13.02 kPa at the same temperature. These values indicate methanol's relatively low and high volatility compared to , facilitating its use in various applications. Methanol is completely miscible with , as well as with alcohols, ethers, and many organic solvents such as and acetone, due to its polar nature and ability to form bonds. Unlike some alcohol-water mixtures, it does not form an , allowing separation by simple . Additional physical metrics include a of 1.3284 at 20 °C, a of 11–12 °C (closed cup), and an of 455 °C. At 20 °C, its dynamic is 0.59 mPa·s, and the surface tension is 22.6 mN/m.
PropertyValueConditionsSource
Density0.7918 g/cm³20 °CNIST WebBook
13.02 kPa20 °CNIST WebBook
1.328420 °C
Dynamic Viscosity0.59 mPa·s20 °CEngineering Toolbox
22.6 mN/m20 °CEngineering Toolbox

Chemical properties

Methanol is a highly polar molecule owing to its hydroxyl (-OH) group, which creates a significant of 1.70 D, facilitating strong intermolecular bonding that influences its reactivity and interactions in solution. This polarity arises from the electronegative oxygen atom pulling toward itself, resulting in a partial negative charge on oxygen and partial positive charges on the carbon and hydrogens. As a weak acid, methanol has a of 15.5 in , indicating limited under neutral conditions, but it can be deprotonated by strong bases to form the methoxide ion (CH₃O⁻). Conversely, methanol exhibits very weak basicity, with a of 754.3 kJ/mol in the gas phase, making to form CH₃OH₂⁺ unfavorable except in highly acidic environments. Methanol's reactivity stems from its functional groups, allowing it to participate in oxidation reactions where it converts to (HCHO) or further to (HCOOH) under appropriate oxidizing conditions. It also undergoes esterification with carboxylic acids in the presence of catalysts like , yielding methyl esters and . Additionally, halogenation reactions with reagents such as or produce (CH₃Cl). The autoionization of methanol follows the equilibrium: $2 \ \ce{CH3OH} \rightleftharpoons \ce{CH3OH2+} + \ce{CH3O-} with an autoprotolysis constant K_{ap} of approximately $10^{-16.7} (or about $2 \times 10^{-17}) at 25°C, reflecting its extremely low ionic conductivity compared to . , methanol displays characteristic absorption bands, including a C-O stretching vibration at approximately 1030 cm⁻¹, which is indicative of its functionality. In ¹H NMR , the methyl protons appear as a around 3.4 , while the hydroxyl proton resonates as a broad near 4-5 , though its exact position varies with concentration and solvent due to hydrogen bonding and exchange. Under normal conditions, methanol remains chemically stable, but at high temperatures (above 500°C), it undergoes primarily to (CO) and gas (H₂) via the endothermic reaction \ce{CH3OH -> CO + 2H2}. This is relevant in studies but requires elevated temperatures without catalysts.

Occurrence

In the interstellar medium

Methanol was first detected in the in 1970 through observations toward B2, marking it as one of the earliest complex organic molecules identified . This discovery highlighted its abundance in molecular clouds, where it serves as a key tracer of dense, star-forming regions. In these environments, methanol forms primarily through two mechanisms: gas-phase reactions, such as the combination of atoms with methoxy radicals (H + CH₃O → CH₃OH), and surface on dust grains involving the successive of (CO) adsorbed onto icy mantles. The grain-surface pathway dominates in cold, dense clouds, where atomic accretes and reacts at low temperatures, leading to methanol-rich ices. Abundance levels vary, with gas-phase abundances up to 10⁻⁶ relative to H₂ in hot corinos, while solid methanol constitutes a few to tens of percent of ice; in comets like Hale-Bopp, it constitutes up to 2% of the volatile content relative to . Astronomers map methanol distributions using its rotational spectral lines, particularly the transitions at 36.2 GHz (J=4₁-3₀ E) and 48.3 GHz, which emit from excited states in warm gas and enable high-resolution imaging of structures. In , methanol acts as a precursor to more complex organic molecules, facilitating the synthesis of prebiotic compounds through further reactions in icy environments. Its deuterated isotopologues, such as CH₂DOH, exhibit high fractionation ratios that signify formation on dust grains at temperatures around 10 K, providing insights into the cold chemistry preceding and formation. Recent observations with the Atacama Large Millimeter/submillimeter Array () up to 2025 have revealed gaseous methanol in protoplanetary disks, such as around , demonstrating both thermal and non-thermal desorption processes that release it from ices into the disk atmosphere. These findings underscore methanol's role in delivering organics to nascent planetary systems.

On Earth

Methanol is naturally produced on through various biological processes, primarily in via the demethylation of in walls catalyzed by pectin methylesterases (PMEs), which releases methanol as a during cell expansion and growth. Emissions rates can reach up to 38 μg g (dry mass)⁻¹ h⁻¹, with increased release upon mechanical damage or . Decaying vegetation also contributes significantly, as microbial breakdown of plant material, including , liberates methanol during in soils and layers. Microbial production further adds to Earth's methanol pool, particularly in anaerobic environments where bacteria reduce CO₂ or degrade to form methanol as an intermediate. For instance, certain bacteria performing nitrate-dependent methane oxidation can produce methanol. In wetlands, methanol concentrations in soils can reach 0.48–2.6 mM due to such microbial activity amid decaying , while in oceans, generate methanol through metabolic pathways, sustaining concentrations around 0.1–0.4 μM in . These microbial sources are balanced by rapid degradation, with ocean bacteria oxidizing methanol to CO₂ at rates of 2–8 nmol L⁻¹ day⁻¹, facilitating its cycling in aquatic and terrestrial ecosystems. Geological sources provide trace amounts of methanol, emitted through volcanic activity and geothermal vents, where high-temperature reactions in fumaroles and hydrothermal systems form it from CO₂ or precursors deep in the . In the atmosphere, methanol maintains global average concentrations of 0.5–5 ppb, reflecting a balance between natural emissions and sinks like oxidation; levels spike to several ppb during biomass burning events, where incomplete of releases large pulses. In oceans and soils, methanol persists at low levels—approximately 0.1–0.4 μM dissolved in and variable in soils—cycling primarily through microbial degradation that converts it back to CO₂, preventing accumulation. The environmental flux of methanol from natural sources is substantial, with annual global emissions estimated at around 100 million tons, predominantly from terrestrial (about 101 Tg yr⁻¹) and oceanic biogenic processes (gross ~24 Tg yr⁻¹), based on 2021 modeling.

History

Early discovery and characterization

In 1661, first isolated pure methanol through the destructive distillation of boxwood, referring to it as the "spirit of box" or "adiaphorus spiritus lignorum" after rectifying crude wood over milk of . This marked the initial laboratory-scale of the compound, obtained as a volatile, distinct from other distillates like acetic acid. Boyle's work laid the groundwork for recognizing methanol as a unique substance derived from , though its chemical nature remained unclear for over a century. During the early 19th century, advancements in enabled more precise characterization. In 1834, and Eugène-Melchior Péligot conducted key experiments on "wood spirit," confirming its elemental composition as carbon, , and oxygen through combustion analysis and derivative preparations. Their studies demonstrated that methanol differed from in reactivity and properties, such as forming distinct ethers and halides, establishing it as a separate rather than a variant of spirit of wine. Dumas and Péligot introduced the term "méthyle" for the radical CH₃, derived from the Greek "methy" (wine) and "hyle" (wood), reflecting its origins; this led to the naming of "methyl alcohol," later shortened to methanol in 1892 by international nomenclature standards. Purification techniques evolved in the mid-19th century with the refinement of , allowing separation of methanol from , acetone, and other wood distillation byproducts through repeated and condensation cycles. By the late 1800s, methanol was widely recognized as the simplest aliphatic , with its structure confirmed as CH₃OH. Early medical applications, such as in solvents and antiseptics, revealed its , including risks of blindness and from ingestion, as documented in pharmacological studies like those by J.F. McFarlan in 1855.

Industrial development

The industrial production of methanol began in the through the , or , of wood, a process that yielded approximately 1-2% methanol by weight from feedstock. This method, often referred to as "wood alcohol" production, supplied small-scale needs for solvents and chemicals until the early , when global output was limited to around 10,000 tons per year due to the labor-intensive nature and low efficiency of wood-based processes. The transition to synthetic production marked a pivotal shift, with initial experiments on (a mixture of and ) dating back to the 1890s, but commercial viability arrived in 1923 with BASF's high-pressure process. This breakthrough utilized a ZnO-Cr₂O₃ catalyst at pressures of 300–400 atm and temperatures of 350–400 °C, enabling efficient conversion of derived primarily from into methanol and scaling production dramatically. Post-World War II advancements further revolutionized the industry; in 1966, (ICI) introduced a low-pressure process employing a Cu/ZnO/Al₂O₃ catalyst, operating at 50–100 atm and 220–260 °C, which reduced energy costs and improved yields, facilitating widespread adoption. Feedstock evolution paralleled these technological leaps, with coal dominating pre-1970s production due to its availability for syngas generation, though it accounted for a significant portion of global output until emerged as the preferred method. By 2000, reforming supplied about 80% of global methanol, driven by lower costs and cleaner processing compared to . remains prominent in specific regions, particularly , where it underpins roughly 40% of worldwide production as of 2025, reflecting the country's resource base and policy support for coal-to-chemicals pathways. Global capacity has expanded exponentially, from modest levels in the to approximately 170 million tons per year by 2024, underscoring methanol's role as a foundational chemical . Projections indicate a 25% capacity increase by 2030, fueled by demand in emerging applications and regional expansions, particularly in the . Key milestones have shaped the industry's trajectory, including the 1980s boom in methyl tert-butyl ether (MTBE) production, which consumed vast methanol volumes as a gasoline oxygenate to meet clean air standards. In the 2010s, China's adoption of methanol-to-olefins (MTO) technology, exemplified by the 2010 startup of the world's first commercial DMTO unit in Baotou, integrated methanol into petrochemical chains and boosted domestic capacity. The 2020s have seen a surge in green methanol initiatives, with over 170 low-carbon projects announced since 2021 to address decarbonization goals through renewable feedstocks like biogas and captured CO₂. In 2025, notable advancements include the validation of the world's largest green methanol project in China and the launch of wind-to-hydrogen methanol facilities, such as the 548 million USD Tiaobinshan project, marking accelerated commercialization of sustainable production.

Production

Conventional production from synthesis gas

The conventional production of methanol primarily relies on the catalytic conversion of synthesis gas (syngas), a mixture of carbon monoxide (CO) and hydrogen (H₂), derived from fossil feedstocks such as natural gas or coal. Syngas is generated through steam reforming of natural gas, where methane reacts with steam to produce CO and H₂ according to the endothermic reaction CH₄ + H₂O → CO + 3H₂, typically at temperatures of 800–1000 °C and pressures of 2–3 MPa over nickel-based catalysts. Alternatively, partial oxidation of coal or heavy hydrocarbons can be employed, involving the reaction of the feedstock with oxygen and steam at high temperatures (1200–1500 °C) to yield syngas with a lower H₂/CO ratio, necessitating adjustment via the water-gas shift reaction (CO + H₂O ⇌ CO₂ + H₂). These methods account for the majority of global methanol output, with natural gas-based routes favored in regions with abundant low-cost gas supplies due to higher efficiency and lower emissions compared to coal gasification. The core methanol synthesis step involves the exothermic of CO (and CO₂) over a catalyst: CO + 2H₂ ⇌ CH₃OH (ΔH = -90.7 kJ/mol), conducted under equilibrium-limited conditions at 5–10 MPa and 230–260 °C to favor conversion while managing heat release. The process requires a stoichiometric H₂/CO ratio of approximately 2:1, achieved by blending streams or incorporating CO₂ (via CO₂ + 3H₂ ⇌ CH₃OH + H₂O). Modern plants employ fixed-bed tubular reactors packed with copper-zinc (Cu/ZnO/Al₂O₃) catalysts, which offer selectivity exceeding 99% toward methanol and operate for 3–5 years before replacement; slurry-phase reactors are used in some large-scale facilities for better heat dissipation. by sulfur compounds, present in raw , is prevented through upstream desulfurization to below 0.1 ppm using zinc absorbers. In a typical process flow, purified is compressed to reaction pressure, preheated, and fed into the synthesis , where per-pass conversion is limited to 20–30% to avoid constraints and hotspots; unreacted gases are recycled after cooling and separation. The , containing 5–15% methanol vapor along with , light hydrocarbons, and inerts, undergoes multistage cooling and to recover crude methanol (70–90% purity), followed by in two or three columns: a pre-distillation column removes lights and dissolved gases, a extracts (boiling point 100 °C), and a final refining column yields high-purity methanol (>99.85 wt%) by separating higher-boiling impurities like . This integrated loop achieves overall carbon efficiency of 90–95%, with tail gas purged to prevent inert buildup. The process is energy-intensive, requiring approximately 30–40 per of methanol, including feedstock (about 28–30 / for ) and utilities for compression, reforming, and distillation; modern optimize via heat integration to approach 31 /. Yields in world-scale facilities reach 5,000–7,000 per day, with global capacity projected at around 116 million per year in 2025, of which approximately 60% derives from and 40% from . vary by feedstock and location, with -based costing 200–300 USD per in 2024, driven by gas prices (typically 3–6 USD/MMBtu) and of 400–600 million USD for a 5,000 tpd plant; -based routes are cheaper in coal-rich areas but incur higher environmental compliance expenses. is the largest producer, accounting for about 50% of global capacity, primarily via , while the contributes about 15–20% through efficient reforming.

Biosynthetic production

Methylotrophic bacteria, particularly aerobic methanotrophs such as Methylococcus capsulatus and Methylosinus trichosporium, naturally oxidize methane to methanol as the first step in their carbon assimilation pathway. This process is catalyzed by methane monooxygenases (MMOs), which insert one oxygen atom from O₂ into methane to form methanol, with the other reduced to water using reducing equivalents from NADH. The key reaction is: \mathrm{CH_4 + O_2 + NADH + H^+ \rightarrow CH_3OH + H_2O + NAD^+} In these organisms, methanol is typically a transient intermediate quickly oxidized further to by (MDH), but accumulation can be achieved under oxygen-limited conditions or by inhibiting MDH activity. For instance, the thermoacidophilic Methylacidiphilum fumariolicum SolV has demonstrated continuous methanol production from , reaching titers of up to 4.1 mM (approximately 0.13 g/L) in cultures under oxygen limitation and without lanthanides that activate MDH. Engineered biosynthetic routes have focused on enhancing methanol production by modifying methanotrophs or introducing pathways into non-native hosts to accumulate methanol from or , rather than further metabolizing it. For example, of Methylosinus trichosporium OB3b has achieved methanol titers of 1.1 g/L from 50% in batch cultures by optimizing expression and MDH inhibition. Efforts to produce methanol from CO₂ or via pathways like the Wood-Ljungdahl pathway in acetogens (e.g., ljungdahlii) have primarily targeted or , with limited direct methanol output due to thermodynamic challenges in reducing CO₂ to methanol anaerobically; however, hybrid approaches combining fermentation with methanol extraction show promise for low-yield C1 conversion. Molybdenum-containing enzymes, such as formate dehydrogenases in some acetogens, play auxiliary roles in utilization but are not central to methanol synthesis. Biosynthetic processes typically involve aerobic or microaerobic in bioreactors, where or serves as the feedstock, and methanol is harvested via gas stripping or to prevent over-oxidation. Yields remain low, ranging from 0.1 to 0.5 g methanol per g substrate consumed, due to competing oxidation pathways, poor gas-to-liquid , and slow microbial growth rates (0.3–0.4 h⁻¹). Advances include adaptive evolution for improved tolerance and multi-stage reactors separating oxidation from growth phases, with lab-scale demonstrations reaching 1 g/L titers. As of 2025, biosynthetic methanol constitutes less than 1% of global production (dominated by at ~100 million metric tons annually), primarily in settings; commercial pilots remain limited to ethanol-focused efforts like those by LanzaTech on off-gases.

Green and sustainable production

Green and sustainable production of methanol emphasizes renewable feedstocks and low-carbon processes to align with global climate objectives, such as reducing in hard-to-abate sectors like chemicals and shipping. These methods leverage renewable , , and captured to produce methanol with near-zero net emissions, contrasting with conventional fossil-based routes that rely on or . Key pathways include e-methanol synthesis via electrochemical reduction and , both of which have seen rapid project announcements amid policy support for decarbonization. As of August 2025, the project pipeline includes 134 e-methanol initiatives with 23.4 million tons capacity by 2030 and 104 biomethanol projects. E-methanol, also known as electro-methanol, is produced through the of captured CO₂ using generated from water electrolysis powered by . The core reaction is the catalytic conversion of CO₂ and H₂ into methanol: \ce{CO2 + 3H2 -> CH3OH + H2O} This process requires high-purity CO₂ from industrial sources or , combined with H₂ from electrolyzers, typically operating at 200–300°C and 50–100 pressure using copper-based catalysts. E-methanol production addresses CO₂ utilization while storing intermittent , making it suitable for scaling with abundant or resources. Biomass-derived methanol involves of lignocellulosic feedstocks, such as residues or , to produce (CO + H₂), followed by conventional . The step occurs at high temperatures (800–1,000°C) in oxygen-steam environments to yield a hydrogen-rich gas, which is then cleaned and converted to methanol via the same catalysts as fossil routes. Typical yields reach approximately 0.4–0.5 tons of methanol per ton of dry , depending on feedstock composition and process efficiency, with overall energy conversion efficiencies of 50–60%. This pathway utilizes sustainable supplies without competing with food production, supporting circular goals. Carbon capture integration enhances by pairing (DAC) or point-source CO₂ with green H₂ for methanol synthesis, enabling negative emissions when using biogenic CO₂. A notable example is the first commercial-scale e-methanol facility in , operational since May 2025, which uses CO₂ from and waste alongside renewable H₂ to produce 42,000 tons annually, demonstrating viable integration of DAC-like capture with . In , Carbon Recycling International's pioneering plant, expanded in recent years, utilizes geothermal-powered and DAC-derived CO₂, though at smaller initial scales of around 4,000–5,000 tons per year, highlighting early commercialization in regions with cheap renewables. These projects underscore the feasibility of CO₂-to-methanol as a technology. Globally, methanol accounted for about 0.2% of total in , with capacity at roughly 0.5 million tons amid overall methanol output of 110 million tons. However, as of July 2025, 230 projects have been announced worldwide, targeting a combined capacity of 41 million tons per year by 2030, driven by demand in shipping and chemicals. The market is projected to grow at a (CAGR) of 34% through 2034, fueled by investments in and capture infrastructure. Key developments include India's first CO₂-to-green methanol plant, announced in November 2024 by Ohmium International in collaboration with Spirare Energy and JNCASR, which integrates electrolyzers with CO₂ capture from a thermal power plant for initial production targeting industrial applications. In the United States, the overall methanol market, including green segments, is valued at USD 5.81 billion in 2025, with capacity growth supported by incentives like the for low-carbon fuels. The has advanced mandates through the FuelEU Maritime regulation, effective from 2025, requiring progressive greenhouse gas intensity reductions for shipping fuels—up to 80% by 2050—positioning green methanol as a compliant drop-in alternative to marine diesel. Economically, green methanol production costs range from 800–1,500 USD per ton in 2025, primarily due to hydrogen expenses, but are expected to decline to 500–800 USD per ton with scaling and cheaper renewables by 2030. Lifecycle emissions for green methanol are below 10 g CO₂ equivalent per MJ, compared to over 50 g CO₂/MJ for fossil-based methanol, enabling up to 90% reductions when accounting for full supply chains including capture and transport. These metrics position green methanol as cost-competitive in carbon-priced markets, particularly for high-value uses like sustainable and maritime fuels.

Applications

Chemical synthesis

Methanol serves as a fundamental building block in the , with approximately 75% of global in 2024 directed toward the synthesis of derivatives such as , acetic acid, and olefins. This utilization underscores its versatility as a C1 feedstock, enabling the of high-volume commodities essential for materials like resins, plastics, and fuels additives. Global methanol demand reached about 91 million metric tons (MMT) in 2023, with chemical applications dominating due to established catalytic processes that convert methanol efficiently under controlled conditions. Formaldehyde is the largest derivative, accounting for roughly 26% of methanol consumption, or approximately 24 MMT annually based on recent demand figures. The primary industrial process involves the of methanol with oxygen: \mathrm{CH_3OH + \frac{1}{2}O_2 \rightarrow HCHO + H_2O} This reaction occurs over silver catalysts at 600–700 °C or iron-molybdate catalysts at 400–500 °C, achieving high selectivity (>90%) in fixed-bed or fluidized-bed reactors. The silver process, historically dominant, operates in excess air to minimize side reactions like complete , while the iron-molybdate route uses steam-diluted feeds for better heat management. Formaldehyde production reached approximately 26 MMT globally in 2024, with methanol comprising over 90% of the feedstock in modern plants. Acetic acid production consumes about 9% of methanol, equivalent to roughly 8 MMT yearly. The , introduced in the 1970s, employs rhodium-iodide for the of methanol: \mathrm{CH_3OH + CO \rightarrow CH_3COOH} Conducted at 150–200 °C and 30–40 atm in a liquid-phase reactor, this method yields >99% selectivity, with iodide promoters enhancing catalyst activity. Modern variants, like the iridium-based Cativa process, further improve efficiency and reduce usage, supporting acetic acid output of over 17 MMT worldwide as of 2024. Methyl tert-butyl ether (MTBE) synthesis utilizes around 11% of methanol, primarily through acid-catalyzed etherification: \mathrm{CH_3OH + (CH_3)_2C=CH_2 \rightarrow (CH_3)_3COCH_3} Ion-exchange resins or zeolites serve as catalysts in reactive columns at 100–150 °C, converting isobutene from streams with >98% . While MTBE production was phased out during the due to groundwater concerns, it remains significant in , where annual capacity exceeds 22 MMT to meet oxygenate demand as of 2024. The methanol-to-olefins (MTO) process, capturing 17% of methanol use, transforms methanol into and (C₂–C₄ olefins) via and over SAPO-34 catalysts at 400–500 °C in fluidized-bed reactors. This non-petrochemical route achieves 80–85% olefin selectivity, with the "hydrocarbon pool" mechanism sustaining the reaction. dominates MTO capacity, operating over 20 MMT annually as of 2024, driven by downstream and production. Other notable syntheses include (DME), which accounts for 6% of methanol consumption through : $2 \mathrm{CH_3OH \rightarrow CH_3OCH_3 + H_2O} This equilibrium-limited reaction uses alumina or catalysts at 250–400 °C, yielding >99% conversion in fixed-bed setups. Methylamines (monomethylamine, , trimethylamine) are produced by reacting methanol with over silica-alumina catalysts at 300–450 °C, with selectivities tuned by feed ratios to favor desired isomers for applications in and pharmaceuticals. These processes collectively highlight methanol's pivotal role in chemical , with ongoing innovations focusing on catalyst stability and .

Fuel applications

Methanol serves as a gasoline additive to enhance octane rating, with blends limited to up to 3% (M3) in the United States and European Union, where it provides a research octane number (RON) boost of approximately 133, improving engine efficiency without significant vehicle modifications. In China, higher blends such as M15 (15% methanol) to M85 (85% methanol) are more prevalent, particularly in provinces like Shanxi and Shaanxi, where over 70,000 taxis have been converted to run on M85 or M100, driven by methanol's lower cost relative to gasoline. These blends reduce carbon monoxide (CO), hydrocarbon (HC), and nitrogen oxide (NOx) emissions compared to pure gasoline, though aldehyde emissions may increase slightly, manageable with catalytic converters; methanol has also aided the phase-out of methyl tert-butyl ether (MTBE) as an oxygenate in reformulated gasoline due to MTBE's groundwater contamination issues. As a direct fuel, methanol is gaining traction in marine shipping to meet International Maritime Organization (IMO) goals for net-zero greenhouse gas emissions by 2050, with a regulatory framework adoption targeted for 2025 to enforce compliance starting in 2028. E-methanol, produced from renewable sources like green hydrogen and captured CO₂, enables zero-carbon operations in dual-fuel vessels; for instance, A.P. Moller-Maersk ordered 18 large dual-fuel methanol container ships in 2024, with over 10 delivered by mid-2025, each capable of carrying over 16,000 TEU and reducing lifecycle GHG emissions by at least 65% compared to fossil fuels. In fuel cell applications, direct cells (DMFCs) oxidize methanol directly at the via the reaction: \mathrm{CH_3OH + H_2O \rightarrow CO_2 + 6H^+ + 6e^-} operating typically at 60–130 °C to balance and methanol crossover. These cells achieve power densities of 100–200 mW/cm², as demonstrated in systems with advanced catalysts yielding up to 181 mW/cm² at 80 °C under low methanol concentrations, making DMFCs suitable for portable and automotive power sources despite challenges like . The methanol-to-gasoline (MTG) process converts methanol to hydrocarbons over ZSM-5 zeolite catalysts at 350–400 °C, following the simplified reaction: \mathrm{CH_3OH \rightarrow \text{hydrocarbons} + \mathrm{H_2O} with high selectivity for gasoline-range products. A commercial demonstration occurred at the New Zealand Synthetic Fuels plant from 1985 to 1997, producing 14,500 barrels per day of gasoline from natural gas-derived methanol, validating the technology's viability for stranded gas resources. Methanol acts as an energy carrier for hydrogen storage through steam reforming: \mathrm{CH_3OH + \mathrm{H_2O \rightleftharpoons CO_2 + 3H_2} (or partial reforming to CO + 2H₂), offering a volumetric energy density of approximately 18.8 MJ/L, over twice that of liquid hydrogen at 8.2 MJ/L, facilitating safer and more efficient transport and on-site generation. As of 2023, energy applications (fuels and biodiesel) account for about 14% of global methanol consumption, with projections indicating growth to around 20% by 2030 driven by adoption of green methanol in transportation sectors. Demand for green methanol in shipping and aviation is projected to rise at a compound annual growth rate (CAGR) of 32% through 2032, driven by decarbonization mandates and scalable production from renewables.

Other uses

Methanol functions as a versatile in numerous applications, particularly for dissolving resins, dyes, and other substances in the of paints, adhesives, and inks. Approximately 10-15% of global methanol production is dedicated to such solvent uses and other miscellaneous applications (including and denaturants) as of 2023, leveraging its ability to mix readily with and many compounds. In manufacturing, methanol serves as the primary reactant in the process, reacting with triglycerides from vegetable oils or animal fats to yield methyl esters and . As a denaturant, methanol is incorporated into at concentrations ranging from 0.5% to 5% by volume, rendering the mixture undrinkable and exempt from beverage taxes for purposes such as agents and fuel additives. This practice is standardized in formulas like specially (SDA) 3-A, which includes 5% methanol to ensure compliance with regulatory requirements. In pharmaceutical production, methanol acts as a solvent for synthesizing vitamins such as B12 and , as well as hormones, antibiotics like , and other active ingredients. At low concentrations, it exhibits properties suitable for certain formulations. High-purity grades of methanol are also utilized for electronic components in manufacturing, where its low residue and effective solvency prevent contamination. Methanol finds niche applications as an additive in washer fluids, typically comprising 30–50% of the mixture to provide freeze protection down to -20°C or lower, and in de-icing solutions for and roadways. Emerging roles include its use as a physical in carbon capture technologies, notably the Rectisol process, which employs chilled methanol to selectively remove CO2 and other acid gases from streams in plants.

Quality and regulatory aspects

Specifications

Methanol specifications vary by intended application, with industry standards ensuring consistent quality, purity, and performance across chemical, , , and reagent uses. The International Methanol Producers and Consumers Association (IMPCA) establishes reference specifications for grade methanol, the most common for and , requiring a minimum purity of 99.85% w/w on a dry basis. This grade limits water content to a maximum of 0.10% w/w to prevent and issues, and to ≤0.5 mg/kg to reduce emissions and . Key impurities such as are restricted to ≤50 mg/kg and acetone to ≤30 mg/kg in formulations, while color is limited to ≤5 Pt-Co units to ensure visual clarity and absence of oxidative degradation products. For solvent applications in electronics and pharmaceuticals, high-purity grades demand ≥99.9% w/w purity, with low metal content (<1 mg/kg total for elements like iron, copper, and lead) to avoid contamination in sensitive manufacturing. This prioritizes minimal non-volatile residues and absorbance properties for clean processing. Fuel grade methanol, aligned with ASTM D1152 for baseline purity (99.85% w/w), limits water to ≤0.10% w/w to maintain combustion stability. Green methanol variants require additional sustainability certifications, such as ISCC EU or RSB, verifying low-carbon feedstocks and emissions reductions through third-party audits.
GradePurity (w/w)Water (max)Key ImpuritiesApplicationsStandard
AA (Fuel/Chemical)≥99.85%0.10%Sulfur ≤0.5 mg/kg; Ethanol ≤50 mg/kg; Acetone ≤30 mg/kgSynthesis, blendingIMPCA Reference Specifications
High-Purity (Solvent)≥99.9%≤0.05%Metals <1 mg/kg total; Non-volatiles ≤1 mg/kgElectronics, pharmaManufacturer specs
Fuel (Blending/Marine)≥99.85%≤0.10%Sulfur ≤0.5 mg/kg; Color ≤5 Pt-CoAutomotive, shippingASTM D1152; ISO 6583:2024
Reagent≥99.8%≤0.1%Acetone ≤20 mg/kg; Residue ≤2 mg/kgLab analysisACS Reagent; ISO 3696 (water for testing)
Reagent grade methanol adheres to ACS standards for analytical work, with purity ≥99.8% and testing often involving compliant with ISO 3696 3 to ensure accuracy in dilutions and extractions. Regional regulations, such as EU REACH, impose impurity controls indirectly through substance registration and restriction dossiers, mandating reporting of contaminants like and ensuring methanol meets Annex XVII limits for safe handling in mixtures. As of 2025, marine fuel standards under ISO 6583:2024 specify three grades: Marine Methanol Grade A (MMA, highest purity with additional requirements), Grade B (MMB, aligned with IMPCA), and Grade C (, wider tolerances), tightening sulfur limits to ≤0.5 mg/kg for all grades to align with global emission controls, including the Mediterranean ECA's 0.1% cap. Traceability requirements for green claims have also strengthened, with certifications like ISCC and RSB mandating or audit trails for feedstock origins and lifecycle emissions. These evolutions support methanol's role in sustainable applications without compromising end-product integrity.

Analysis methods

Gas chromatography (GC), particularly with flame ionization detection (FID), serves as the primary analytical technique for detecting and quantifying impurities in methanol, such as higher alcohols and trace hydrocarbons, at parts-per-million (ppm) levels. This method separates volatile components based on their interaction with a stationary phase, allowing precise identification and measurement of contaminants that could affect methanol's use in or fuels. For instance, standards like ASTM D7920 outline GC procedures to assess impurities in fuel-grade methanol, ensuring compliance with quality thresholds by resolving peaks for compounds like or acetone with detection limits below 10 ppm. While GC-FID excels for organic impurities, thermal conductivity detection (TCD) variants can also quantify water content in the low ppm range, though it is less sensitive for alcohols compared to FID. Karl Fischer titration remains the gold standard for determining content in methanol, offering high accuracy across a wide range from 0.01% to 100%, with coulometric variants achieving detection limits as low as 10 for trace moisture. The method involves dissolving the sample in an methanol-based medium and titrating with iodine-containing reagent, where the reaction stoichiometrically consumes to form methyl and other products, enabling detection via electrometric or colorimetric means. This technique is essential for in methanol production, as even minor contamination can catalyze side reactions in downstream applications. Coulometric Karl Fischer is preferred for ultra-low levels in high-purity grades, providing results with relative standard deviations under 2%. Spectroscopic methods complement chromatographic techniques for targeted impurity analysis and structural verification in methanol. Ultraviolet-visible (UV-Vis) spectroscopy detects aldehydes, such as formaldehyde, by measuring absorbance at approximately 340 nm, where carbonyl groups exhibit characteristic n-π* transitions, allowing quantification of trace levels (down to 1 ppm) without sample preparation. Nuclear magnetic resonance (NMR) spectroscopy, particularly ¹H-NMR, confirms methanol's structural integrity by identifying the distinct singlet peaks for the methyl (δ ≈ 3.4 ppm) and hydroxyl (δ ≈ 4.8 ppm, variable due to hydrogen bonding) protons, while also detecting impurities like ethanol through additional multiplet signals. These non-destructive methods are widely used in research and quality assurance, with NMR providing quantitative purity assessments via integration ratios when internal standards are employed. Additional techniques address specific impurities beyond volatiles. (HPLC) with UV detection quantifies acetates, such as , in methanol by separating polar compounds on reversed-phase columns, achieving resolutions for concentrations from 0.1% to trace levels. (ICP-MS) determines metal contaminants, like sodium or iron, at sub-ppm levels by ionizing the sample in an and analyzing mass-to-charge ratios, crucial for preventing catalytic poisoning in . Simpler physical measurements, including and , serve as rapid bulk checks for overall composition, correlating deviations from standard values (e.g., density 0.791 g/mL at 20°C) to potential . For real-time process control in production facilities, on-line enables continuous monitoring of methanol purity by analyzing vibrational spectra, where characteristic C-O stretch bands at around 1030 cm⁻¹ distinguish methanol from or impurities without sampling disruptions. This non-invasive approach supports immediate adjustments in gas conversion, maintaining product consistency at scales from to industrial. Regulatory standards guide these analyses, with EPA Method 8260 specifying GC-MS protocols for volatile organics in environmental samples containing methanol, ensuring detection of associated impurities like at low ppb levels. Modern laboratory norms achieve accuracies of ±0.01% for major components like methanol itself, reflecting advancements in and traceable to NIST standards.

Safety

Toxicity

Methanol is metabolized primarily in the liver through oxidation by to , which is rapidly converted by to ; this metabolite inhibits mitochondrial , disrupting and leading to tissue , particularly in the and brain. The biological half-life of methanol in human blood is approximately 2–3 hours under normal conditions, though this can be prolonged by or metabolic saturation. Acute exposure to methanol produces severe toxic effects via , , or dermal , with inhalation LC50 values reported at 41,000 ppm (approximately 54 g/m³) in mice over 6 hours, indicating high potency in mammalian models. Symptoms typically emerge after a latent period of 12–24 hours and include , vomiting, abdominal pain, and ; visual disturbances such as , , and snowfield vision arise from formic acid-induced optic nerve damage, with blindness possible at ingested doses of 3–10 g in humans. Chronic exposure to methanol can result in cumulative damage to the liver and kidneys, manifesting as elevated liver enzymes and renal tubular dysfunction with prolonged low-level contact. Occupational exposure limits are established to mitigate these risks, with the OSHA (PEL) set at 200 ppm as an 8-hour time-weighted average, the ACGIH (TLV) at 200 ppm (8-hour TWA) and 250 ppm (STEL) as of 2025, and the NIOSH immediately dangerous to life or health (IDLH) concentration at 6,000 ppm. In humans, ingestion of as little as 30 mL of pure methanol can be fatal due to severe from accumulation, which is exacerbated in individuals with as hepatic tetrahydrofolate is required for to . Vulnerable populations, including children due to lower body mass and immature metabolic pathways, and alcoholics from induced activity leading to faster toxic formation, face heightened risks of severe outcomes from even sublethal exposures. Methanol is not classified as a by the International Agency for Research on Cancer (IARC Group 3), indicating inadequate evidence of carcinogenicity in humans. Biomonitoring of exposure often involves measurement of urinary formate levels, which correlate with internal dose and aid in assessing occupational risks. Its volatility facilitates as a primary route in industrial settings. Management of methanol poisoning focuses on inhibiting metabolism, correcting acidosis, and removing the toxin. is the preferred to block , with as an alternative; folinic acid or folic acid enhances formate elimination; addresses acidosis; and is indicated for severe cases or methanol levels >50 mg/dL.

Fire and explosion hazards

Methanol is classified as a Class IB flammable liquid under NFPA 30 standards, characterized by a below 22.8°C (73°F) and a at or above 37.8°C (100°F), indicating high ignitability at ambient temperatures. Its vapors form mixtures with air, with a lower explosive limit (LEL) of 6% by volume and an upper explosive limit (UEL) of 36% by volume, allowing ignition over a wide concentration range. A distinctive hazard is that methanol flames are nearly invisible in daylight, complicating detection and increasing the risk of unnoticed spread. Explosion risks are particularly acute from vapor cloud formation in confined or poorly ventilated spaces, where methanol's low minimum ignition of 0.14 enables ignition from minor sparks, such as those from or mechanical equipment. The is 464°C (867°F), meaning sustained heat sources can trigger combustion without an open . These properties necessitate careful control of ignition sources during transfer, storage, or processing to prevent vapor accumulation leading to or . Safe handling requires storage in well-ventilated areas to disperse vapors, using grounded metal containers or approved non-sparking equipment to minimize static buildup, as methanol's conductivity can generate electrostatic charges during flow. It is incompatible with strong oxidizers, such as peroxides or , which can cause violent reactions or accelerated . with NFPA 30 guidelines for Class IB liquids dictates limitations on container sizes, separation distances from ignition sources, and fire-resistant construction for storage facilities. In the event of a fire, appropriate extinguishing agents include dry chemical, carbon dioxide (CO₂), or alcohol-resistant foam, as water alone may spread burning liquid without fully suppressing vapors. For spills, methanol evaporates quickly due to its high vapor pressure, but residual liquid poses slip hazards and persistent ignition risks from lingering vapors; containment with absorbent materials and ventilation is essential to avoid vapor cloud formation. Regulatory classifications designate methanol as UN 1230, a Class 3 flammable liquid under U.S. (DOT) rules, requiring specific packaging, labeling, and placarding for transport. For green methanol variants used in sustainable applications, 2025 updates in guidelines maintain similar flammability profiles but introduce enhanced protocols for systems, including improved and crew to address equivalent volatility and fire risks. Historical incidents in chemical plants during the underscored as a key ignition source during methanol handling and transfer, often resulting in vapor ignitions and fires that prompted stricter grounding and requirements. Modern mitigation relies on continuous monitoring with flame detectors, gas sensors, and automated shutdown systems, substantially reducing the incidence of such events in contemporary facilities.