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| HS Code | 166381 |
| Chemical Formula | C6H5OH |
| Molar Mass | 94.11 g/mol |
| Appearance | White crystalline solid |
| Odor | Sweet and tarry |
| Density | 1.07 g/cm3 |
| Melting Point | 40.5 °C |
| Boiling Point | 181.7 °C |
| Solubility In Water | 8.3 g/100 mL at 20 °C |
| Pka | 10.0 |
| Flash Point | 79 °C |
| Autoignition Temperature | 715 °C |
| Vapor Pressure | 0.35 mmHg at 20 °C |
As an accredited Phenol factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | 25 kg packed in lined steel drums, securely sealed, with hazard labeling and corrosion-resistant packaging. |
| Container Loading (20′ FCL) | Load phenol drums into 20' FCL, secure tightly, label as hazardous, ensure ventilation and spill containment. |
| Shipping | Phenol ships as a hazardous material—UN1671 (solid) or UN2312 (molten), Class 6.1, Packing Group II. Use leak-proof, corrosion-resistant containers with toxic hazard labels. Segregate from foodstuffs and oxidizers. Comply with IMDG, ADR, or IATA regulations, and ensure proper shipping documentation and emergency response information accompany the consignment. |
| Storage | Phenol must be stored in a cool, dry, well-ventilated area away from heat, sparks, and direct sunlight. Keep in tightly sealed, corrosion-resistant containers (e.g., dark glass or stainless steel) within secondary containment. Segregate from strong oxidizers, bases, and foodstuffs. If solidified, warm gently. Store below 40°C but above its melting point, with clear hazard labeling. |
| Shelf Life | Phenol has a typical shelf life of 2 years when stored tightly sealed, protected from light, and kept in a cool, dry area. |
Condensation of phenol with acetone in a fixed-bed ion-exchange reactor remains the dominant industrial route to 4,4′-isopropylidenediphenol, commonly referred to as BPA. The reaction is typically carried out at a phenol-to-acetone molar feed ratio between 5:1 and 10:1 over sulfonated polystyrene-divinylbenzene resin at 60 °C to 80 °C; excess phenol suppresses the formation of o,p-BPA, trisphenol, and Dianin’s compound. Acetone conversion across a production bed is maintained above 98 % with a liquid hourly space velocity in the range of 0.2 h⁻¹ to 0.5 h⁻¹, and the crude reactor output is processed through a phenol recovery train that includes vacuum distillation, adduct crystallization, and rotary vacuum filtration. The 1:1 phenol-BPA adduct is crystallized from the phenol-rich mother liquor, separated, and decomposed to release BPA, while residual phenol is recycled to the fixed-bed inlet; this recycle loop is a critical operating constraint because water generated during condensation accumulates and poisons the acid resin. Polycarbonate-grade BPA is controlled under ASTM D4297-15 for p,p-BPA content and molten Pt-Co color, and melt transesterification with diphenyl carbonate requires residual water in the BPA feed to be held below 50 ppm to prevent hydrolysis of the carbonate raw material.
BPA derived from this route enters two major downstream chains: interfacial polymerization with phosgene or melt-phase reaction with diphenyl carbonate for polycarbonate, and advancement with epichlorohydrin for liquid epoxy resins. For food-contact epoxy coatings, the specific migration limit set by Regulation (EU) 2018/213 is 0.05 mg/kg for BPA in varnishes and coatings, which drives resin producers to specify low free BPA in epoxy batches. Production-scale fixed-bed reactors exhibit catalyst deactivation over campaigns of 12 to 18 months in continuous service, and the deactivation profile is normally managed by progressive temperature ramping of 5 °C to 10 °C across the bed until acetone breakthrough exceeds specification. Batch-to-batch variance in phenol feedstock iron content is controlled below 0.1 mg/kg because iron accelerates sulfonic acid resin oxidation and contributes to off-color byproducts that are difficult to remove in the final melt crystallization step.
Acetone oligomerization byproducts such as mesityl oxide and diacetone alcohol also form under acid resin conditions, and their accumulation in the phenol recycle stream can reduce BPA color quality if not purged. The purification sequence therefore includes a light-ends stripper and a wiped-film evaporator to remove low boilers before adduct crystallization. A centrifugal or rotary vacuum filter with cloth under a nitrogen blanket handles the adduct crystal cake; cake washing with pure phenol at 55 °C to 65 °C is used to displace mother liquor containing o,p-BPA. During adduct decomposition, residual phenol is recovered in a packed column operated under vacuum at reboiler temperatures not exceeding 180 °C, above which BPA degradation and color formation increase. These temperature limits represent operational boundaries rather than optional settings.
The acid-catalysed reaction of phenol with formaldehyde at a phenol-to-formaldehyde mole ratio below unity yields novolac, a solid thermoplastic phenolic oligomer that is cured with hexamethylenetetramine, commonly introduced at 6 phr to 12 phr. Industrial novolac kettles charge phenol, 37 % formalin, and oxalic acid at 0.5 wt% to 1.5 wt% of the phenol charge, followed by reflux condensation at 95 °C to 100 °C and vacuum dehydration at 140 °C to 160 °C. The free phenol content of the finished flake is measured by ISO 8975 and is commonly held below 0.5 wt% to limit emissions during compounding and molding. Molding compounds formulated from novolac, wood flour or mineral fillers, and hexamine display a characteristic DSC curing exotherm beginning near 150 °C and peaking between 160 °C and 180 °C; this narrow processing window defines the injection molding barrel profile, which is kept below 90 °C in the feed zone and below 105 °C at the nozzle to prevent premature crosslinking. Reciprocating screw machines with 14:1 to 18:1 L/D and compression ratios near 1.4:1 are used for glass-reinforced phenolic compound, while mold temperatures are held at 170 °C to 190 °C to complete cure within 30 s/mm to 60 s/mm wall thickness.
Phenolic molding compounds are specified for commutator segments, brake pistons, pump impellers, and electrical switch housings, where property compliance is verified through ASTM D5948 or ISO 14526-2 for flexural strength, Izod impact, and water absorption. The hexamine cure reaction releases ammonia and formaldehyde decomposition products, and high shear dispersion in a twin-screw compounding extruder can increase stock temperature beyond the onset of cure if screw speed exceeds 300 min⁻¹ for a 40:1 L/D barrel. Production compounding lines therefore use barrel zones held between 70 °C and 85 °C with liquid-cooled screw cores; this is a known processing bottleneck when highly filled compounds are run at higher throughput. Resole resins, in contrast to novolacs, are produced with a phenol-to-formaldehyde mole ratio of 1:1.2 to 1:3.0 and an alkaline catalyst such as sodium hydroxide, and their liquid or B-staged forms are used in decorative laminates, plywood adhesives, and insulation binders. The viscosity drift of resole resin at storage temperatures of 5 °C is retested by cone-and-plate viscometer before impregnation to avoid changes in prepreg resin pickup and final laminate thickness.
Selective hydrogenation of phenol to cyclohexanone is operated in both gas-phase fixed-bed reactors with palladium-on-alumina and liquid-phase continuous stirred or fixed-bed units with nickel-based catalysts. The kinetic bottleneck is not phenol conversion but the consecutive hydrogenation of cyclohexanone to cyclohexanol, which becomes pronounced above 0.5 MPa hydrogen partial pressure on nickel and above 210 °C in gas-phase operation. Industrial gas-phase units maintain bed temperatures of 170 °C to 210 °C and hydrogen-to-phenol mole ratios of 4:1 to 8:1, using multi-tubular reactors with molten-salt cooling to manage a strongly exothermic reaction; the heat release requires careful inlet temperature control because a 10 °C excursion can shift selectivity rapidly toward cyclohexanol and over-reduced byproducts. The condensate from the reactor outlet is distilled to separate cyclohexanone, cyclohexanol, and unreacted phenol, and the recycle of unconverted phenol is critical to maintain overall yield above 95 % across a catalyst campaign.
Cyclohexanone entering caprolactam manufacture via hydroxylamine oximation and Beckmann rearrangement must meet low-water and low-acid specifications, with water content determined by ISO 760 Karl Fischer titration and held below 0.05 wt% to avoid oxime hydrolysis. Cyclohexanol/cyclohexanone mixtures, known as KA oil, are oxidized with nitric acid to adipic acid, and vent gas abatement for nitrous oxide is required under process safety and environmental permits. In liquid-phase phenol hydrogenation, the catalyst deactivation mode is frequently metal sintering and carbonaceous fouling, and regeneration requires controlled air treatment below 400 °C; published data for specific selectivities below 0.2 MPa hydrogen pressure are limited because most licensing data are held as confidential process information. Production-scale pressure vessels are designed to 2.5 MPa despite operating pressures of 1.0 MPa to 1.5 MPa, providing relief margin for exothermic runaway scenarios.
Before ethoxylation, the alkylated phenol stream is stripped of unreacted phenol and high-boiling alkylate byproducts by vacuum distillation, because residual phenol influences the ethylene oxide addition distribution and the final surfactant color. Alkylation of phenol with branched nonene is carried out over a sulfonated ion-exchange resin or boron trifluoride complex at 80 °C to 120 °C, with a phenol-to-olefin mole ratio of 1.2:1 to 2.0:1; lower reaction temperatures favor para-substitution, while higher temperatures shift the isomer distribution toward ortho and increase dialkylate formation. The reactor is exothermic, and industrial fixed-bed resin units use interstage cooling or oil-jacketed tubular reactors to keep the temperature rise below 15 °C per pass. After distillation, the nonylphenol product is ethoxylated with ethylene oxide under potassium hydroxide catalysis in a pressurized stirred autoclave at 140 °C to 170 °C, producing nonylphenol ethoxylates with average EO chain lengths of 4 to 12. Placement on the EU market of nonylphenol and nonylphenol ethoxylates as substances or in mixtures is restricted under REACH Annex XVII entry 46, which establishes a concentration limit of 0.1 % w/w for many water-dispersive and cleaning applications; industrial users verify formulations by LC-MS or GC-MS before bulk transfer.
The following cross-reference is applied to batch release and regulatory compliance for the principal downstream products.
| Application | Relevant standard or regulation | Controlled parameter | Typical limit or test basis |
|---|---|---|---|
| BPA for food-contact epoxy coatings | Regulation (EU) 2018/213 | Specific migration limit for BPA | 0.05 mg/kg |
| BPA monomer purity | ASTM D4297-15 | p,p-BPA content and molten Pt-Co color | Specification values per standard |
| Phenolic novolac free phenol | ISO 8975 | Free phenol in resin | Commonly 0.5 wt% maximum |
| Phenolic molding compound | ASTM D5948 / ISO 14526-2 | Flexural strength, Izod impact, water absorption | Grade-dependent |
| Caprolactam-grade cyclohexanone | ISO 760 | Water content | 0.05 wt% maximum |
| Nonylphenol ethoxylate formulations | REACH Annex XVII entry 46 | NP/NPE concentration | 0.1 % w/w maximum for restricted uses |
Because phenol chlorination is exothermic and the monochloro-to-dichloro selectivity window is narrow, reactor temperature is normally held between 50 °C and 100 °C and chlorine feed is staged to limit local chlorine concentration. The reaction proceeds with ferric chloride or aluminum chloride as halogenation catalyst, and the ortho-to-para chlorophenol ratio is shifted toward para by polar solvents and lower temperature, while extended chlorine-to-phenol mole ratios approaching 2.0:1 favor 2,4-dichlorophenol. 2,4-Dichlorophenol is the primary intermediate for 2,4-dichlorophenoxyacetic acid, produced by condensation with sodium chloroacetate under alkaline conditions; the herbicide active substance is subject to approval under Regulation (EC) No 1107/2009 and to residue limits set under country-specific MRL frameworks. Production equipment uses enamel-lined stirred reactors and chlorine gas handling systems with scrubbing on pressure relief, because the chlorinated phenols are corrosive and the off-gas contains hydrogen chloride that must be recovered by adiabatic absorption. Published data for catalyst-specific selectivity under fully industrial configurations is limited; process licensors typically optimize chlorine staging and solvent selection in pilot campaigns rather than in open literature.
For salicylic acid production, the sodium phenate feed is dried to a water content below 0.2 wt% before carbonation because water in the solid feed leads to sodium hydroxide formation and lower carbonation yield. The Kolbe-Schmitt carboxylation of sodium phenoxide is conducted under carbon dioxide pressure in a heated kneader reactor or rotary furnace, with temperatures of 120 °C to 140 °C favoring the ortho-carboxylate product, while sustained heating above 200 °C shifts the product distribution toward para-hydroxybenzoic acid. Reactor pressure is maintained in the range of 0.8 MPa to 1.5 MPa, and the solid mass is kneaded continuously to expose fresh sodium phenate surface to carbon dioxide; this mass-transfer constraint is the principal throughput limitation in batch and continuous kneader designs. The resulting sodium salicylate is acidified with sulfuric acid, and crude salicylic acid is recrystallized to meet Ph. Eur. salicylic acid monograph and USP Salicylic Acid specifications, with assay by titration commonly in the range 99.5 % to 101.0 % on the dried basis.
Salicylic acid is acetylated with acetic anhydride to acetylsalicylic acid in a jacketed stirred reactor, with the exotherm controlled below 85 °C to limit hydrolysis of the anhydride and to avoid diacetyl impurity formation. Methyl salicylate is produced by esterification with methanol under acid catalysis and is tested by gas chromatography against a reference standard; the ester is used as a topical counterirritant and as a flavoring intermediate. The remaining unreacted phenol from sodium phenate preparation is recovered by distillation and recycled, while sodium sulfate generated during acidification is removed by filtration and washed to reduce organic carryover. Because the Kolbe-Schmitt reaction operates in a heterogeneous solid-gas regime, batch-to-batch yield variation is strongly dependent on the particle size distribution of the dried sodium phenate; manufacturers typically mill the dried salt to a mean particle size below 250 µm before carbonation to reduce diffusion resistance and shorten cycle time.
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Phenol, CAS 108-95-2, C₆H₅OH, relative molecular mass 94.11 g/mol, is supplied as a refined hydroxylated aromatic intermediate rather than as a model-numbered formulated product. Commercial differentiation is made by physical form—low-iron molten liquid maintained at 50–65 °C in insulated 316L stainless steel tank containers, or crystalline solid in steel drums at ambient temperature—and by the solidification-point, water, and colour parameters of ASTM D2439. A typical high-purity grade shows solidification point not less than 40.6 °C, water content not more than 0.10 wt%, and APHA colour not above 20 Pt-Co. Crystalline phenol has a density of 1.07 g/cm³ at 25 °C; molten phenol density is approximately 1.05 g/cm³ at 50 °C. Water solubility is 8.3 g/100 mL at 25 °C. Above the phenol-water upper critical solution temperature of approximately 66 °C, water and phenol form a single liquid phase; below this temperature, phase separation occurs in wet streams.
Refined phenol is differentiated from technical-grade streams primarily by water, colour, and trace carbonyls. A typical high-purity grade is specified by solidification point not less than 40.6 °C, water content not more than 0.10 wt%, and APHA colour not above 20 according to ASTM D2439; polymer-grade phenol for bisphenol A units may add limits for iron below 1 mg/kg and total carbonyls below 50 mg/kg. Colour is measured by ASTM D1209 in Pt-Co units, and water is determined by Karl Fischer titration under ASTM E203 or an equivalent internal procedure. Technical-grade material from cumene cleavage may contain acetic acid, acetol, cumyl alcohol, and α-methylstyrene; if the purification column is operated with insufficient reflux, these components depress the solidification point and raise final colour above customer limits.
Analytical quality-control laboratories quantify phenol purity by capillary gas chromatography with flame ionization detection; the limit of quantitation for trace cumene and α-methylstyrene is typically below 50 mg/kg. Solidification point is a sensitive bulk-purity indicator because small amounts of water or non-aromatic impurities can depress the melting point measurably. In practice, a solidification point below 40.4 °C frequently indicates either water ingress or incomplete removal of cumene-derived co-products.
In the Hock process, cumene is oxidised at 90–130 °C and 4–8 bar to cumene hydroperoxide; oxidation is deliberately stopped below 25 wt% hydroperoxide concentration to limit side reactions. Cleavage with sulfuric acid in continuous stirred reactors at 50–80 °C produces phenol and acetone at a mass ratio of approximately 0.62 kg acetone per 1 kg phenol. Downstream distillation trains operate under vacuum to keep base temperatures below 140 °C; higher reboiler wall temperatures increase tar formation and shorten run length between shutdowns. In production-scale distillation trains, reboiler heat-transfer surfaces are designed for low flux and high circulation to prevent local overheating and phenol tar deposition.
The purification train usually begins with a cumene column to recover unreacted cumene, followed by a phenol column and an acetone column. The phenol column base temperature is kept below 140 °C; vacuum systems are often liquid ring pumps, but phenol contamination in the seal water requires steam stripping before discharge to meet wastewater limits. The residue stream, known as phenol tar, may be cracked thermally at 250–300 °C to recover additional phenol from heavy aromatic compounds.
Molten phenol freezes at approximately 40.9 °C; therefore transfer lines, storage tanks, and pumps are normally maintained at 55–65 °C. Jacketed or heat-traced 316L stainless steel piping is standard because carbon steel contributes iron and darkens the product. External steam tracing above 80 °C is avoided because prolonged heating increases colour and generates volatile impurities. Pumps used for molten phenol are typically rotary positive-displacement units with mechanical seals; packed pumps are avoided because gland leakage crystallises and raises workplace concentrations above the 5 ppm 8-hour TWA limit. Storage tanks are nitrogen-blanketed at 0.005–0.010 barg to exclude oxygen and moisture. Water ingress above 0.1 wt% lowers the solidification point but promotes corrosion and hazy resin batches.
Above 66 °C, phenol and water form a single liquid phase; below that temperature, phenol-rich and water-rich phases separate, complicating reflux control in dehydration columns. Vacuum dehydration of wet phenol streams is performed at 80–120 mmHg absolute and 70–90 °C to minimise overhead phenol loss.
The largest single downstream consumption of phenol is bisphenol A synthesis. In continuous BPA units using sulfonated styrene-divinylbenzene ion-exchange resin, the feed molar ratio of phenol to acetone is maintained between 6:1 and 12:1, reactor temperature is held at 60–75 °C, and liquid hourly space velocity is maintained at 0.5–1.0 h-1. Excess phenol is recovered by distillation and recycled; dehydration of the recycle stream is critical because water above 2 wt% in the reaction section reduces condensation rate and increases by-product formation. Recovered phenol is passed through a purge distillation column to reject heavy oligomers. Published data for this specific purge configuration is limited to unit-specific licensor operating manuals, but the process principle is standard across ion-exchange-catalysed plants.
Phenolic resole resins are made with alkaline catalysts at phenol-to-formaldehyde molar ratios from 1:1.0 to 1:2.2; temperature is held at 60–80 °C and the reaction is quenched by cooling to below 20 °C for storage-stable low-free-phenol grades. Resole batches with residual free phenol above 0.5 wt% are avoided in low-emission laminating systems because free phenol contributes to workplace exposure during lay-up. Novolac resins are produced at 1:0.75 to 1:0.85 phenol-to-formaldehyde molar ratios with oxalic acid or sulfuric acid at 90–100 °C; vacuum dehydration reduces water below 1 wt% before flaking or pastillation. Novolac molding compounds are compounded with hexamethylenetetramine at 8–12 phr in twin-screw extruders with L/D 40–48 and barrel temperatures 80–110 °C; the screw configuration is selected for low shear to avoid premature crosslinking. In a plant that processes both resin types, reactor vent condensers are segregated because acidic and alkaline vapours combine to form corrosive deposits and accelerate vessel wall thinning.
Phenol is hydrogenated to cyclohexanone over supported nickel or palladium at 130–170 °C and 1–5 bar for caprolactam routes; selectivity above 90% to cyclohexanone is required to limit cyclohexanol by-product. Alkylphenol producers react phenol with propylene trimer or isobutylene over acid catalysts at 100–140 °C, yielding nonylphenol or tertiary-butylphenol for ethoxylates and resins. These applications tolerate technical-grade phenol with higher water content and colour than BPA-grade material, but not high levels of neutralisation salts, which deactivate the acid catalysts.
Phenol differs from cresol isomers by the absence of the methyl substituent, which lowers boiling point by about 20 °C and increases the number of unsubstituted reactive ring positions. Compared with catechol, the single hydroxyl group reduces water solubility from roughly 45 g/100 mL to 8.3 g/100 mL at 25 °C and avoids ortho-dihydroxy metal chelation that can discolour resin systems. Resorcinol is a meta-dihydroxy compound whose reactions with formaldehyde proceed much faster than phenol, limiting its use to cold-setting adhesives; phenol remains the lower-cost structural monomer for bulk resins. Table 1 compares the principal physical properties.
| Property | Phenol | p-Cresol | Catechol | Resorcinol |
|---|---|---|---|---|
| Melting point (°C) | 40.9 | 34.7 | 105 | 110 |
| Boiling point (°C) | 181.7 | 202.3 | 245.5 | 281 |
| pKa at 25 °C | 9.99 | 10.26 | 9.45 | 9.32 |
| Water solubility (g/100 mL) | 8.3 | 2.4 | 45 | 110 |
Industrial exposure benchmarks are summarised in Table 2. Phenol is classified under CLP Regulation (EC) No 1272/2008 as acute toxic by oral, dermal, and inhalation routes and as corrosive to skin; the dermal notation applies because liquid phenol is absorbed through skin. Closed-cup flash point is 79 °C, autoignition temperature is 715 °C, and explosive limits are 1.8–8.6 vol% in air. At concentrations above the NIOSH IDLH value, supplied-air respiratory protection is required during vessel entry or spill response.
| Benchmark | Value | Notation |
|---|---|---|
| OSHA PEL 8-h TWA | 5 ppm | skin notation |
| NIOSH REL 8-h TWA | 5 ppm | skin notation |
| ACGIH TLV 8-h TWA | 5 ppm | skin notation |
| NIOSH IDLH | 250 ppm | — |
| Closed-cup flash point | 79 °C | No open-flame handling |
| Lower explosive limit | 1.8 vol% | air |
| Upper explosive limit | 8.6 vol% | air |
Substitution or interchange between phenol and resorcinol in adhesives is not direct because resorcinol’s higher reactivity requires slower formaldehyde addition and lower condensation temperature to avoid runaway gelation. In plants switching between the two monomers, washable or dedicated mixing lines are used to prevent residual resorcinol from accelerating subsequent phenol-formaldehyde batches.