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M-Cresol
M-Cresol
from Wikipedia
m-Cresol
m-cresol
m-cresol
3D model of m-cresol
3D model of m-cresol
Names
IUPAC name
3-methylphenol
Other names
3-Cresol
m-Cresol
3-Hydroxytoluene
m-Cresylic acid
1-Hydroxy-3-methylbenzene
3-Methylbenzenol
Identifiers
3D model (JSmol)
506719
ChEBI
ChEMBL
ChemSpider
DrugBank
ECHA InfoCard 100.003.253 Edit this at Wikidata
EC Number
  • 203-39-4
101411
KEGG
RTECS number
  • GO6125000
UNII
  • InChI=1S/C7H8O/c1-6-3-2-4-7(8)5-6/h2-5,8H,1H3 ☒N
    Key: RLSSMJSEOOYNOY-UHFFFAOYSA-N ☒N
  • InChI=1/C7H8O/c1-6-3-2-4-7(8)5-6/h2-5,8H,1H3
    Key: RLSSMJSEOOYNOY-UHFFFAOYAJ
  • Cc1cc(O)ccc1
Properties
C7H8O
Molar mass 108.14 g/mol
Appearance colorless liquid to yellowish liquid
Density 1.034 g/cm3, liquid at 20 °C
Melting point 11 °C (52 °F; 284 K)
Boiling point 202.8 °C (397.0 °F; 475.9 K)
2.35 g/100 ml at 20 °C
5.8 g/100 ml at 100 °C
Solubility in ethanol miscible
Solubility in diethyl ether miscible
Vapor pressure 0.14 mmHg (20 °C)[1]
−72.02×10−6 cm3/mol
1.5398
Viscosity 6.1 cP at 40 °C
Hazards
Occupational safety and health (OHS/OSH):
Main hazards
May cause serious burns. Very destructive of mucous membranes. Harmful if inhaled. Toxic in contact with the skin or if swallowed.
GHS labelling:
GHS05: CorrosiveGHS06: ToxicGHS08: Health hazard
Danger
H227, H301, H311, H314, H351, H370, H372, H373, H401
P201, P202, P210, P260, P264, P270, P273, P280, P281, P301+P310, P301+P330+P331, P302+P352, P303+P361+P353, P304+P340, P305+P351+P338, P307+P311, P308+P313, P310, P312, P314, P321, P322, P330, P361, P363, P370+P378, P403+P235, P405, P501
NFPA 704 (fire diamond)
NFPA 704 four-colored diamondHealth 3: Short exposure could cause serious temporary or residual injury. E.g. chlorine gasFlammability 2: Must be moderately heated or exposed to relatively high ambient temperature before ignition can occur. Flash point between 38 and 93 °C (100 and 200 °F). E.g. diesel fuelInstability 0: Normally stable, even under fire exposure conditions, and is not reactive with water. E.g. liquid nitrogenSpecial hazards (white): no code
3
2
0
Flash point 86 °C
Explosive limits 1.1%–? (149 °C)[1]
Lethal dose or concentration (LD, LC):
242 mg/kg (oral, rat, 1969)
2020 mg/kg (oral, rat, 1944)
828 mg/kg (oral, mouse)[2]
NIOSH (US health exposure limits):
PEL (Permissible)
TWA 5 ppm (22 mg/m3) [skin][1]
REL (Recommended)
TWA 2.3 ppm (10 mg/m3)[1]
IDLH (Immediate danger)
250 ppm[1]
Safety data sheet (SDS) External MSDS
Related compounds
Related phenols
o-cresol, p-cresol, phenol
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
☒N verify (what is checkY☒N ?)

meta-Cresol, also 3-methylphenol, is an organic compound with the formula CH3C6H4(OH). It is a colourless, viscous liquid that is used as an intermediate in the production of other chemicals. It is a derivative of phenol and is an isomer of p-cresol and o-cresol.[3]

Production

[edit]

Together with many other compounds, m-cresol is traditionally extracted from coal tar, the volatile materials obtained in the production of coke from (bituminous) coal. This residue contains a few percent by weight of phenol and isomeric cresols. In the cymene–cresol process, toluene is alkylated with propylene to give isomers of cymene, which can be oxidatively dealkylated analogous to the cumene process. Another method, involves carbonylation of a mixture of methallyl chloride and acetylene in the presence of nickel carbonyl.[3]

Applications

[edit]

m-Cresol is a precursor to numerous compounds. Important applications include:

C7H8O + C3H6C10H14O

Natural occurrences

[edit]

m-Cresol is a component found in temporal glands secretions during musth in male African elephants (Loxodonta africana).[7]

m-Cresol is a constituent of tobacco smoke.[8]

m-Cresol is a component found in secretions from the ant Colobopsis saundersi during Autothysis.[9][10]

See also

[edit]

References

[edit]
[edit]
Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
m-Cresol, also known as 3-methylphenol, is an with the molecular formula C₇H₈O, serving as one of the three isomeric forms of , where the is positioned meta to the hydroxyl group on the benzene ring. It appears as a colorless to pale yellow liquid with a characteristic tarry, phenolic odor and is moderately soluble in . m-Cresol exhibits key physical properties including a melting point of 11–12 °C, a boiling point of 202 °C, and a density of 1.03 g/cm³ at 20 °C, making it a viscous liquid at room temperature that solidifies upon cooling. Chemically, it is stable under normal conditions but sensitive to light, air, and heat, potentially darkening over time; it reacts vigorously with strong oxidizers, bases, and certain acids like nitric acid. Its pKa value of approximately 10.01 indicates weak acidity, typical of phenols. Industrial production of m-cresol primarily involves from or fractions, where it occurs naturally alongside ortho- and para-isomers, followed by separation via or sulfonation methods. Synthetic routes include chlorination or sulfonation of , followed by to yield the meta isomer selectively. Global production volumes are significant, with annual outputs in the exceeding 10,000 tonnes, mainly for use in polymers and chemical manufacturing. As a versatile chemical intermediate, m-cresol is widely employed in the synthesis of pesticides such as fenthion and fenitrothion, antioxidants, synthetic (via methylation to 2,3,6-trimethylphenol), herbicides, fumigants, and resins. It also functions as a and in products like and certain insulin formulations, and finds applications in photographic developers, explosives, and fragrances due to its solvent properties. Additionally, trace amounts occur naturally in some foods, tobacco smoke, and as a metabolite in biological systems. m-Cresol poses significant health and environmental hazards; it is toxic if swallowed or absorbed through the skin, causing severe burns, eye damage, and potential central nervous system depression. Acute oral toxicity in rats shows an LD50 of 242–2,020 mg/kg, and it is classified as a possible human carcinogen (Group C) with experimental evidence of neoplastic effects. Environmentally, it is harmful to aquatic life with long-lasting effects and exhibits moderate mobility in soil. Occupational exposure limits include a TLV of 20 mg/m³, emphasizing the need for protective measures in handling.

Properties

Physical properties

m-Cresol, systematically named 3-methylphenol, is an with the molecular formula C₇H₈O and a of 108.14 g/mol. Its structure consists of a phenol ring substituted with a at the meta position. The compound appears as a colorless to yellowish at . Key physical properties of m-cresol are summarized in the following table:
PropertyValueConditions
1.034 g/cm³20 °C
Melting point11.8 °C-
Boiling point202.2 °C1013 hPa
Flash point86 °CClosed cup
Vapor pressure0.11 mmHg25 °C
Viscosity12.9 mPa·s25 °C
These values are derived from experimental measurements and indicate m-cresol's state under ambient conditions, with a relatively low allowing it to remain fluid near . m-Cresol exhibits moderate in , approximately 2.3 g/100 mL at 20 °C, and is fully miscible with and . Compared to its isomers, m-cresol has a intermediate between (191 °C) and p-cresol (202 °C).

Chemical properties

m-Cresol, as a phenolic compound, displays moderate acidity attributable to the phenolic hydroxyl group, which can dissociate to form a resonance-stabilized phenoxide . The pKa of this group is approximately 10.1 at 25°C. This value is slightly higher than that of unsubstituted phenol (pKa ≈ 10.0), rendering m-cresol a marginally weaker acid due to the electron-donating of the meta-methyl , which reduces the stability of the conjugate base without significant involvement. In reactions, the hydroxyl group strongly activates the ring and directs incoming electrophiles to the ortho and para positions relative to itself (positions 2, 4, and 6). The meta-methyl group provides additional activation through and inductive effects, preferentially directing to its own ortho and para positions (2, 4, and 6), thereby enhancing overall reactivity at these shared sites compared to phenol alone. This cooperative directing effect makes m-cresol highly susceptible to substitutions such as , , and sulfonation under mild conditions. m-Cresol exhibits notable sensitivity to oxidation, especially when exposed to air or oxidizing agents, resulting in the formation of colored impurities such as derivatives. This reactivity stems from the ease with which the phenolic ring undergoes oxidative coupling or dehydrogenation to yield para-quinoid structures, a common behavior among that can lead to discoloration in stored samples. The structural features of m-cresol enable significant hydrogen bonding interactions, primarily through the hydroxyl group acting as both a donor and acceptor, which promotes self-association in neat liquid or solution and enhances in protic solvents. The contributes modestly via weak C-H···O interactions, influencing intermolecular packing and in binary mixtures. Spectroscopically, m-cresol is characterized by a broad O-H stretching band in the infrared spectrum at approximately 3300–3350 cm⁻¹, indicative of hydrogen-bonded phenolic hydroxyl groups. In ¹H NMR (in CDCl₃ or similar solvents), the methyl protons appear as a singlet at δ ≈ 2.3 ppm, the aromatic protons resonate as a complex multiplet between δ 6.7 and 7.3 ppm (with distinct signals for H-2, H-4, H-5, and H-6), and the OH proton signal varies widely (δ 4–12 ppm) depending on concentration, solvent, and hydrogen bonding.

Production

Industrial production

m-Cresol is primarily produced industrially through extraction from and various synthetic routes, with the former serving as a traditional source and the latter enabling larger-scale, controlled production. In extraction, high-temperature coke oven from processes contains a of , including cresols where m-cresol constitutes approximately 40-45% of the total cresols (typically a few percent of the overall ). The is first fractionally distilled to isolate the phenolic fraction (boiling range ~180-220°C), followed by alkaline extraction with to form sodium phenates, acidification to liberate the crude , and further purification via or sulfonation to separate isomers based on differing reactivity—m-cresol and p-cresol form monosulfonic acids more readily than o-cresol, allowing selective isolation. Synthetic production of m-cresol often involves the alkaline of mixtures, a variant of the Raschig-Hooker process adapted from phenol synthesis; (prepared by chlorination of ) are hydrolyzed under high temperature and pressure with caustic soda, yielding a cresol mixture enriched in m-cresol (up to 60-70% selectivity). Alternatively, methylation of phenol with over acidic catalysts (e.g., alumina or zeolites) at 300-450°C produces a mixture of isomers (o:m:p ratios ~40:30:30), which is then separated. The cymene process, analogous to the route for phenol, involves alkylation of with to form m-cymene, followed by air oxidation to the and acid-catalyzed cleavage to m-cresol and acetone, though this is less common for the meta isomer compared to the para variant. Global production capacity for m-cresol exceeds 60,000 metric tons per year as of 2024, representing a significant portion of total output (estimated at around 150,000-200,000 tons annually across all isomers), with major producers including ( and ), (), and SI Group (). Isomer separation from mixed streams is challenging due to close boiling points (m-cresol 202.9°C, p-cresol 201.9°C, 191.0°C), making energy-intensive (often requiring multi-stage columns with high reflux ratios and energy inputs of 5-10 GJ/ton) and yields typically 80-95% after purification via adsorption, , or sulfonation-desulfonation sequences to achieve >99% purity.

Laboratory synthesis

One established laboratory method for synthesizing m-cresol involves the of methallyl chloride with and , catalyzed by nickel carbonyl. This reaction is carried out under mild pressure and temperature conditions in a suitable , yielding m-cresol in approximately 80% efficiency. Selective methylation of phenol with over acidic catalysts, such as MCM-22 with a SiO₂/Al₂O₃ ratio of 25–30, provides another route to m-cresol. The gas-phase reaction occurs at around 300°C in a fixed-bed reactor, resulting in ~40% phenol conversion and >95% selectivity to cresols, with m-cresol comprising up to 50% of the cresol products due to the influence of strong Brønsted acid sites. Isomer-specific isolation of m-cresol from the mixture is achieved through or preparative . m-Cresol can be obtained by reducing m-hydroxybenzaldehyde (3-hydroxybenzaldehyde) via the Wolff–Kishner reaction, which employs hydrazine hydrate and under in a high-boiling like , converting the aldehyde to the methyl group with good yields typical for aromatic aldehydes. A classical sequence for m-cresol begins with commercially available m-nitrotoluene or m-toluidine (noting that direct of yields only ~3-4% m-nitrotoluene), followed by reduction to m-toluidine using iron or catalytic if starting from the nitro compound, and then diazotization with in acidic medium at low temperature (~0°C) followed by hydrolytic decomposition in refluxing benzene-water mixture. This final step from m-toluidine affords m-cresol in 87% yield with >99.5% purity after neutralization and rectification. Regardless of the synthetic route, purification to laboratory-grade standards (>99% purity) is routinely performed using under reduced pressure (e.g., 10–20 mmHg at 80–100°C) to minimize , or with hexane-ethyl acetate eluents for analytical samples. Standard laboratory equipment, including round-bottom flasks, condensers, and rotary evaporators, suffices for these scales, though pressurized setups are required for .

Applications

Synthetic applications

m-Cresol serves as a key starting material in , particularly for producing pharmaceuticals and fine chemicals through electrophilic aromatic substitutions that leverage its phenolic reactivity. The meta-positioned influences , often favoring ortho-functionalization relative to the hydroxyl group due to steric hindrance at the adjacent position. One prominent application is the synthesis of , a monoterpenoid phenol used as an and in pharmaceuticals. is produced via the acid-catalyzed of m-cresol with in the gas phase, typically over or alumina catalysts at 200–300°C and 1–5 bar pressure, following the reaction C₇H₈O + C₃H₆ → C₁₀H₁₄O. This process achieves m-cresol conversions of up to 80% with thymol selectivities around 75–87%, depending on catalyst and conditions. The favors the 6-position (ortho to OH, meta to CH₃) due to the steric bulk of the meta-methyl group, which hinders substitution at the 2-position between the OH and CH₃ substituents, directing the isopropyl group to form 2-isopropyl-5-methylphenol (). This method originated in the early , with foundational work by Niederl and Natelson in 1936 demonstrating the intramolecular rearrangement of m-cresyl ethers or direct under acidic conditions to yield and its isomers. m-Cresol is also employed in the synthesis of antioxidants and through of the aromatic ring. introduces nitro groups, primarily at the 4- or 6-position, yielding intermediates like 4-nitro-m-cresol, which serve as precursors for phenolic antioxidants and certain contact . For instance, mixtures of m- and p-cresol undergo to produce antioxidants such as alkylated nitro-phenols, while pure m-cresol supports insecticide formulations, with 4-nitro-m-cresol used in the synthesis of the insecticide fenitrothion. Sulfonation, another electrophilic process, functionalizes m-cresol at ortho or para positions to form sulfonic acids. In the production of (), m-cresol is transformed into trimethylhydroquinone (TMHQ) intermediates via sequential and oxidation, followed by with isophytol. The process begins with ortho/para-directed of m-cresol to 2,3,6-trimethylphenol, exploiting the meta-methyl to enhance selectivity at unhindered ortho sites, yielding TMHQ after oxidation; this chromanol precursor then undergoes acid-catalyzed condensation with isophytol to form . This route, widely adopted industrially, highlights m-cresol's in stereoselective reactions for synthesis.

Material science applications

m-Cresol undergoes copolymerization with to produce m-cresol-formaldehyde resins, which serve as key components in adhesives and coatings for composite materials. These resins are particularly employed in surface modification of fibers to enhance interfacial in rubber composites, such as those used in tires, conveyor belts, and V-belts. Compared to traditional resorcinol-formaldehyde-latex systems, m-cresol-formaldehyde offers a less toxic alternative while maintaining strong bonding performance. Optimal formulations, such as a cresol-to-formaldehyde molar ratio of 1:2 and a resin-to-latex weight ratio of 0.23, yield peeling forces up to 7.3 N per sample and H-pull-out forces of 56.8 N, with fiber breaking strength reduced by less than 5%. Curing typically occurs at 180–200°C, enabling efficient processing for industrial applications. In conductive polymers, m-cresol functions as a secondary doping agent for , particularly in its emeraldine salt form when primarily doped with . This secondary doping induces a conformational shift from a compact coil to an extended coil structure, significantly enhancing , in organic solvents, and film-forming capabilities. As a result, films cast from m-cresol solutions exhibit conductivities exceeding 10³ S/cm, far surpassing those obtained from solvents like or N-methyl-2-pyrrolidinone, where residual solvent content remains around 15 wt% post-evaporation. This improvement supports applications in and sensors, with crystallinity reaching approximately 50% and domain sizes of ~50 Å. m-Cresol-based terpolymers, such as those formed with and or , are utilized in chelating ion-exchange resins for selective of heavy metal ions from aqueous solutions. These resins demonstrate high affinity for ions like Cu²⁺ and Pb²⁺, facilitating processes. Additionally, derivatives like , synthesized from m-cresol and phosphorus oxychloride, act as flame-retardant plasticizers and stabilizers in (PVC) formulations, improving thermal stability and flexibility in vinyl plastics without compromising mechanical integrity. Recent developments since 2010 have explored m-cresol derivatives in enzyme-mediated to create bio-inspired phenolic polymers with potential for sustainable materials, though biodegradability remains limited compared to aliphatic polyesters.

Occurrence

Biological sources

m-Cresol is secreted by male African elephants (Loxodonta africana) from their temporal s during , a periodic state of heightened and reproductive activity, where it serves as a component of pheromonal signals for communication and dominance display. Studies of temporal gland secretions have identified m-cresol alongside p-cresol and phenol, with its presence varying by sample but contributing to the overall volatile profile that conveys status to other elephants. In certain ant species, notably (synonym Camponotus saundersi), m-cresol is a key constituent of mandibular secretions expelled during defensive , a suicidal behavior where workers rupture their bodies to release toxic fluids that deter predators and protect the colony. This compound acts as a corrosive within a mixture that includes , 6-methylsalicylic acid, and 2,4-dihydroxyacetophenone, with m-cresol comprising a major portion—up to significant levels approaching 10% in related exploding taxa—enhancing the secretion's and repellent properties. m-Cresol also occurs naturally in tobacco smoke, arising from the of and other components during , where it forms alongside other like and p-cresol through thermal breakdown of phenolic precursors in leaves. This process mimics natural degradation but is biologically rooted in the lignin structure of Nicotiana plants. Trace amounts of m-cresol are found naturally in various foods, including shoots, beans, and spices, derived from in materials. It also appears as a minor metabolite of in biological systems, such as in human urine following exposure, where is hydroxylated to form cresol isomers including m-cresol. Biosynthesis routes for m-cresol in natural organisms remain understudied, unlike the better-characterized p-cresol pathway from .

Environmental presence

m-Cresol occurs naturally as a fossil-derived in and deposits, where it is obtained through processes such as of crude oil and of . Trace levels appear in coal-derived materials as natural analogs from ancient lignins. It is also present in crude oil and as a component of these natural mixtures. In industrial settings, m-cresol is detected in wastewater from operations and phenolic resin production, with concentrations ranging from approximately 2.7 mg/L to 950 mg/L in effluents and up to 1,230 mg/L in processes. For example, raw wastewater has been reported to contain m-cresol at levels around 183 mg/L. m-Cresol undergoes rapid biodegradation in soil under aerobic conditions, primarily by microorganisms such as Pseudomonas putida, with a reported half-life of about 0.6 days in uncultivated grassland surface soil. Its environmental distribution is influenced by a log Kow of 1.94, indicating moderate hydrophobicity, and a soil adsorption coefficient (Koc) ranging from 22 to 3,420, which promotes partitioning into soil organic matter over water but allows some mobility depending on soil pH and type. Volatilization from soil and water is limited due to a low Henry's law constant (approximately 1.2 × 10−6 atm-m³/mol). Monitoring data from U.S. Environmental Protection Agency (EPA) and related assessments indicate low ambient levels of cresols, including m-cresol, in air near industrial sites, with concentrations of 0.3–3.3 μg/m³ reported near wood treatment facilities and a national median of 1.59 μg/m³ in ambient air samples. In sediments and soils, m-cresol is only occasionally detected, mainly at sites contaminated by spills or , at levels such as 1,400 μg/L in associated , owing to its rapid aerobic degradation. reports similarly note infrequent detections in sediments, emphasizing its persistence under anaerobic conditions but overall transience in oxic environments.

Safety and regulation

Health effects

m-Cresol poses significant health risks through various exposure routes, primarily dermal absorption and inhalation, where it is harmful upon skin contact and toxic if breathed in. It is readily absorbed through the skin due to its moderate water solubility, allowing penetration and systemic distribution. Under the Globally Harmonized System of Classification and Labelling of Chemicals (GHS), m-cresol is designated as toxic if swallowed (H301), toxic in contact with skin (H311), and causing severe skin burns and eye damage (H314). Acute exposure to m-cresol is highly corrosive to the skin, eyes, and mucous membranes, resulting in chemical burns, severe irritation, and potential tissue damage. Inhalation leads to irritation, including symptoms such as coughing, , and in severe cases, . Oral ingestion exhibits acute toxicity with an LD50 of 242 mg/kg in rats, manifesting in symptoms like , , , convulsions, and organ damage, particularly to the , liver, and kidneys. Chronic exposure to m-cresol may cause liver and damage, as evidenced by increased organ weights and histopathological changes in animal studies. Cresols, including m-cresol, have not been classified by the International Agency for Research on Cancer (IARC) with respect to their carcinogenicity to humans due to inadequate evidence; however, the U.S. Environmental Protection Agency (EPA) designates them as possible human carcinogens ().

Environmental and regulatory aspects

m-Cresol exhibits moderate to aquatic organisms, with a 96-hour LC50 of 13 mg/L reported for ( mykiss). It is also harmful to , showing a 48-hour of 22 mg/L for water flea (), and to , with a 72-hour of 29 mg/L for Pseudokirchneriella subcapitata. These values indicate potential ecological risks in contaminated water bodies, though m-cresol demonstrates low bioaccumulation potential due to its log Kow of 1.96 and rapid metabolism in . Under the EU REACH regulation, m-cresol is registered and classified as acutely toxic to aquatic life (Aquatic Acute 1) and causing long-term adverse effects (Aquatic Chronic 2), requiring risk assessments for environmental releases. In the United States, it is listed as a by the EPA and designated a hazardous substance under CERCLA. In , as of February 2025, m-cresol is listed as a restricted in under 's Cosmetic Ingredient Hotlist. For occupational exposure, NIOSH recommends a REL of 2.3 ppm (10 mg/m³) as an 8-hour , with a PEL of 5 ppm (22 mg/m³) (skin notation) set by OSHA, and an IDLH of 250 ppm; these limits stem from observed respiratory and dermal effects in workers. Waste containing m-cresol is managed as hazardous under RCRA, assigned code U052 for unused commercial products and D024 under the toxicity characteristic with a regulatory level of 200 mg/L. Recent evaluations in the , including under EU REACH criteria, have concluded that m-cresol does not possess endocrine-disrupting properties.

References

  1. https://.ncbi.nlm.nih.gov/compound/M-Cresol
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