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Cyclohexanone

is an with the molecular formula C₆H₁₀O, consisting of a six-membered carbon ring with a , appearing as a colorless to pale yellow liquid with a peppermint-like odor. It has a molecular weight of 98.14 g/mol, a of -47 °C, a of 155.6 °C, a of 0.9478 g/mL at 20 °C, and is soluble in (approximately 8.6 g/100 mL at 20 °C) as well as miscible with most solvents. is primarily produced on an industrial scale through the of , which yields a mixture of and , followed by separation and purification steps such as or dehydrogenation of the alcohol component. Alternatively, it can be synthesized via the of phenol, though this route is less common. The compound serves as a key chemical intermediate, with over 95% of global production directed toward the manufacture of precursors: specifically, conversion to for nylon-6 and to for nylon-6,6 via oxidation and further processing. Remaining applications include its use as a versatile in the formulation of paints, lacquers, resins, inks, and adhesives, as well as in the production of pharmaceuticals, pesticides, and plasticizers. Cyclohexanone is classified as a ( 44 °C) and poses risks including to the eyes, , and , with potential for upon or ; it is or inhaled and requires careful handling in industrial settings. The International Agency for Research on Cancer (IARC) has not classified it as carcinogenic to humans (Group 3).

Properties

Physical properties

Cyclohexanone is an with the molecular formula C₆H₁₀O, consisting of a six-membered carbocyclic with a . It appears as a colorless to pale yellow oily liquid possessing a - or acetone-like . Key physical properties of cyclohexanone are summarized in the following table:
PropertyValueConditions
Molar mass98.14 g/mol-
Melting point-47 °C-
Boiling point155 °C101.3 kPa
Density0.947 g/cm³20 °C
Refractive index1.450720 °C
Vapor pressure5 mmHg25 °C
Cyclohexanone exhibits slight solubility in water, approximately 8.6 g/100 mL at 20 °C, while being miscible with common organic solvents including , , and acetone. Thermodynamic properties include a of 45.1 kJ/mol and a liquid of 177 J/mol·K at 27 °C. Cyclohexanone occurs in trace amounts in cigarette smoke and serves as a urinary in humans following exposure to xenobiotics.

Chemical properties

Cyclohexanone features a (C=O) where the carbon atom is sp² hybridized, forming a planar with the surrounding atoms and exhibiting bond lengths of approximately 1.21 for the C=O and 1.50 for the adjacent C-C bonds. This configuration contributes to a significant of about 2.9 D, arising from the polarity of the C=O . The alpha-hydrogens in cyclohexanone are moderately acidic, with a pKa value ≈ 18-20, which facilitates enolization through to form resonance-stabilized ions. The carbonyl oxygen is weakly basic, capable of coordinating with acids but not exhibiting strong . In , cyclohexanone displays a characteristic C=O stretching absorption at 1715 cm⁻¹, indicative of the unconjugated functionality. Proton NMR reveals the alpha-methylene protons at approximately 2.3 ppm, shifted downfield due to deshielding by the carbonyl, while the other ring methylene protons appear between 1.6 and 2.0 ppm. In ¹³C NMR, the carbonyl carbon resonates at around 208 ppm, reflecting its electron-deficient nature. Cyclohexanone exhibits thermal stability up to temperatures exceeding 300 °C before significant occurs, though it is susceptible to under acidic conditions via self-condensation mechanisms. As a typical , cyclohexanone undergoes reactions at the electrophilic carbonyl carbon and alpha-deprotonation under conditions to generate enolates for further reactivity. It also absorbs ultraviolet light at approximately 280 due to the forbidden n→π* involving the carbonyl oxygen's non-bonding electrons.

History and synthesis

Discovery

Cyclohexanone was first identified in 1888 by German chemist Edmund Drechsel during experiments involving the of phenol dissolved in a slightly acidified using . Among the mixture of products formed, Drechsel isolated a new compound, which he named "hydrophenoketone" based on its presumed origin from phenol. He proposed that the substance arose through a sequence of and oxidation steps during the electrolytic process. Early characterization efforts by Drechsel confirmed the compound's ketonic functionality when it reacted with to yield an derivative, a standard test for carbonyl groups at the time. This reaction, along with and determination, supported its identification as a simple aliphatic . The , recognized as a six-carbon ring with a ketone group (C₆H₁₀O), was established in the late through comparative studies with known cyclic compounds and degradation reactions. In the pre-20th century era, cyclohexanone appeared sporadically as a byproduct in various experiments, such as distillations or oxidations involving cyclic hydrocarbons, but its scarcity from these low-yield sources limited any practical applications. Researchers primarily viewed it as a curiosity in the expanding field of alicyclic chemistry rather than a compound of immediate utility.

Laboratory synthesis

In laboratory settings, cyclohexanone is commonly synthesized through the oxidation of , a secondary , using as the Jones reagent, prepared from (CrO₃) dissolved in aqueous and acetone. This method selectively converts the alcohol to the under mild conditions, typically at , with the reaction proceeding via chromate ester formation followed by elimination of water. Yields for this oxidation are typically around 90%, making it a reliable approach for small-scale preparations. The balanced equation for the process is: \ce{C6H11OH + [O] -> C6H10O + H2O} An alternative oxidation employs (PCC) in as the reagent, which offers the advantage of avoiding over-oxidation and is particularly suitable for conditions. PCC, formed from , , and , oxidizes secondary alcohols to ketones with high selectivity and minimal side products, achieving yields of approximately 80-90%. This method is often preferred in research labs for its compatibility with acid-sensitive substrates. For milder conditions, can be oxidized using (NaOCl) in acetic acid, known as the Chapman-Stevens oxidation, where household serves as a convenient source of the oxidant. The acetic acid generates in , which facilitates the transformation at ambient temperature without requiring heavy metal catalysts, yielding 84-89% of cyclohexanone. This approach is valued in educational and contexts for its accessibility and reduced toxicity. A direct synthesis from involves photochemical oxidation with air using sensitizers like to generate , though this method is less practical due to low yields, often below 10%, and requires setups. It proceeds via intermediates but is mainly exploratory rather than routine. Regardless of the method, the crude cyclohexanone is purified by under reduced pressure to separate it from unreacted , , and byproducts, taking advantage of its of approximately 155°C at to minimize .

Industrial production

The dominant industrial method for producing cyclohexanone involves the catalytic oxidation of with air to form a of cyclohexanol and cyclohexanone known as KA oil, followed by dehydrogenation of the to yield primarily cyclohexanone. This two-step process accounts for the majority of global production due to its economic viability and integration with precursor manufacturing. In the first step, is oxidized in the liquid phase at 140–160 °C and 10–15 bar pressure using homogeneous catalysts such as (II) or naphthenates, achieving a conversion of approximately 5–10% per pass with a selectivity of about 80–85% to KA oil. The reaction proceeds via a free-radical mechanism, producing KA oil with a typical cyclohexanol-to-cyclohexanone ratio of 4:1. The KA oil is then subjected to catalytic dehydrogenation, often using zinc oxide or palladium-based catalysts at 250–300 °C, converting the cyclohexanol component to cyclohexanone while recycling unreacted . An alternative route is the direct of phenol to cyclohexanone, which is employed in regions with abundant phenol supply from processes. This liquid-phase reaction uses or catalysts supported on carbon or alumina, conducted at 120–150 °C and 1–10 hydrogen pressure, with high selectivity (>95%) to cyclohexanone under optimized conditions. The balanced equation for this transformation is: \mathrm{C_6H_5OH + 2 H_2 \rightarrow C_6H_{10}O} This method offers advantages in terms of lower oxidation byproducts but is less common globally due to higher hydrogen consumption and phenol feedstock costs compared to the KA oil route. Emerging processes aim to improve and integration by starting from . One such approach, developed by , involves hydroalkylation of to cyclohexylbenzene using a bifunctional catalyst (e.g., on ), followed by air oxidation to the and acid-catalyzed cleavage to co-produce phenol and cyclohexanone. This route has seen pilot-scale demonstrations and potential commercial implementations in the , offering higher atom efficiency and reduced waste compared to traditional methods. Global production of cyclohexanone is estimated at approximately 3.7 million metric tons per year as of 2022, with projections for steady growth driven by demand; major producing regions include (over 50% share), the , and . Leading producers such as , Fibrant, and have focused on energy efficiency enhancements through integrated KA oil processing, including heat recovery and catalyst recycling, reducing overall by up to 20% in modern facilities.

Uses and reactions

Industrial applications

Cyclohexanone serves as a key intermediate in the industrial production of polymers, accounting for approximately 85% of its global consumption as of 2023 in the synthesis of and . In the manufacture of , cyclohexanone—typically as part of a mixture known as KA oil (cyclohexanone and )—is oxidized to using as the oxidant. This process generates , which is then polymerized with to form , widely used in textiles, automotive parts, and engineering plastics. For production, cyclohexanone is converted to cyclohexanone oxime by reaction with , followed by the to yield , the monomer for . Approximately 90% of worldwide is produced via this cyclohexanone-based route as of 2023. Global cyclohexanone consumption for these nylon applications reached about 3.3 million metric tons in 2023, driven by demand in the automotive and textile sectors. Beyond nylon precursors, approximately 10% of cyclohexanone production is utilized as a solvent in the formulation of paints, inks, resins, and adhesives, owing to its ability to dissolve ethers, polymers, and other resins effectively. It also finds minor applications as an intermediate in the synthesis of herbicides and in the production of cyclohexanone-formaldehyde resins, which are employed in coatings and printing inks.

Other reactions

Cyclohexanone reacts with (NH₂OH) to form cyclohexanone , a key intermediate in various synthetic transformations. This condensation typically occurs under mildly acidic or neutral conditions, proceeding via of the hydroxylamine nitrogen to the carbonyl carbon, followed by dehydration. The resulting serves as a precursor for the , where treatment with an acid catalyst, such as or , induces migration of the anti-alkyl group to the , yielding ε-caprolactam. The of this rearrangement stems from the anti migration aptitude, where the group trans to the hydroxyl moiety preferentially migrates, ensuring high selectivity in the formation of the product. Similarly, cyclohexanone undergoes condensation with to form the corresponding , which is a crucial step in the Wolff-Kishner reduction for to . of the carbonyl to a secondary yields , achievable through mild hydride transfer using (NaBH₄) in protic solvents like or , often at room temperature with high yields exceeding 90%. Catalytic over metal catalysts, such as or on carbon, also efficiently converts cyclohexanone to under moderate hydrogen pressure, achieving complete selectivity to the . For complete to the methylene group, forming , the Clemmensen reduction employs zinc amalgam in concentrated under refluxing conditions, effectively cleaving the C=O bond in acidic media. Alternatively, the Wolff-Kishner reduction utilizes the intermediate treated with a strong base like at elevated temperatures, proceeding via a mechanism to afford the in good yields. Alpha-functionalization of cyclohexanone begins with at the alpha position using strong bases like (LDA) at low temperatures to generate the kinetic , which can then be with primary alkyl halides to introduce substituents selectively at the alpha carbon. This is widely used in due to its and compatibility with unsymmetrical ketones. In the , treatment of cyclohexanone with halogens (e.g., iodine or ) in aqueous base leads to oxidative cleavage, albeit less efficiently than for methyl ketones, ultimately forming as the dicarboxylic product through ring opening. The Baeyer-Villiger oxidation transforms into ε-caprolactone using peracids such as (mCPBA) in , inserting an oxygen atom adjacent to the carbonyl. In this symmetrical case, the reaction proceeds smoothly with the secondary alkyl groups exhibiting equivalent , but in general, favors migration of the more substituted group, placing the oxygen on the less substituted side of the original . Photochemical reactions of cyclohexanone include the Paterno-Büchi [2+2] , where UV irradiation of the in the presence of aldehydes or alkenes generates spirocyclic oxetanes through excitation of the carbonyl to its , followed by addition to the π-bond of the partner. This reaction highlights the synthetic utility of cyclohexanone in constructing strained four-membered rings for natural product synthesis.

Illicit use

Cyclohexanone serves as a key precursor in the illicit production of (), a Schedule II classified as a . In syntheses, cyclohexanone is converted to 1-piperidinocyclohexanecarbonitrile through reaction with and , followed by a with to yield . This route has been documented in forensic analyses of seized materials since the 1970s, when emerged as a street drug. Cyclohexanone is also employed as an intermediate in the synthesis of , another , through processes involving bromination of derived cyclohexanone compounds and subsequent cyclization with o-chlorobenzonitrile or related . These methods exploit cyclohexanone's availability as an industrial solvent and , facilitating small-scale operations in hidden laboratories. In the United States, cyclohexanone falls under monitoring as a chemical associated with production and is included on the agency's Special Surveillance List to track potential diversions from legitimate commerce. Clandestine labs producing or often rely on diverted industrial supplies, with detection complicated by cyclohexanone's volatile solvent properties, which produce a distinctive minty that operators may attempt to mask during production. Under the 1988 United Nations Convention against Illicit Traffic in Narcotic Drugs and Psychotropic Substances, precursors like those used in and synthesis are subject to international monitoring, though cyclohexanone itself is not listed in Tables I or II; the (INCB) reports occasional seizures linked to its diversion for illicit drug manufacture. For instance, in 2014, U.S. authorities seized 20 liters associated with labs, indicating limited but persistent diversion from industrial sources estimated at less than 1% of global production in the .

Safety and environmental impact

Health hazards

Cyclohexanone primarily enters the through in occupational environments, where it is commonly used as a , though absorption and are also possible routes of . Acute causes to the eyes, , and , often manifesting as redness, burning sensations, and coughing upon contact or . of vapors can lead to effects such as , , , and , with higher concentrations potentially causing or narcosis. Animal studies indicate moderate , with an oral LD50 of 1,620 mg/kg in rats, a dermal LD50 of 1,100 mg/kg in rabbits, and an LC50 of 8,000 (4 hours) in rats. Prolonged or repeated exposure to cyclohexanone is associated with potential neurotoxic effects such as and , as well as liver and kidney damage observed in animal studies at elevated doses. The International Agency for Research on Cancer (IARC) classifies cyclohexanone as Group 3, not classifiable as to its carcinogenicity to s, with no clear evidence of carcinogenic potential in available data. Regarding , high-dose animal exposures have shown maternal and fetal toxicity without significant malformations, suggesting possible risks at extreme levels but limited data. Occupational exposure is regulated to minimize these risks, with the American of Governmental Industrial Hygienists (ACGIH) recommending a (TLV) of 20 as an 8-hour time-weighted average and 50 short-term exposure limit, with skin notation due to absorption concerns. For immediate management of exposure, first aid measures include flushing affected eyes with copious amounts of for at least 15 minutes while holding eyelids open, and removing contaminated clothing followed by thorough skin washing; in cases of , move the individual to with adequate to disperse vapors and seek medical attention if symptoms persist.

Environmental considerations

Cyclohexanone is readily biodegradable in environments, achieving 83-96% degradation within 28 days according to 301F manometric respirometry tests using inoculum. This rapid , combined with its in of approximately 3.1 days due to volatilization and low soil adsorption (log Koc = 1.82), indicates low persistence in soil and systems. In air, it degrades primarily through reaction with photochemically produced hydroxyl radicals, with an estimated of 1-2 days, and supplementary direct photolysis contributing a of about 4.3 days. Bioaccumulation potential is minimal, as evidenced by its low (log Kow = 0.81), which suggests negligible uptake in organisms. Aquatic toxicity of cyclohexanone is moderate, with 96-hour LC50 values for fish species such as (Pimephales promelas) ranging from 527 to 732 mg/L and golden orfe (Leuciscus idus) at 536-752 mg/L. For invertebrates, the 24-hour EC50 for exceeds 800 mg/L, while algal growth inhibition (EC50 for Desmodesmus subspicatus) is reported above 100 mg/L in 72-hour tests, confirming it does not pose high risk to primary producers at environmentally relevant concentrations. These profiles support its classification as not toxic (T) under REACH criteria. As a (), cyclohexanone contributes to photochemical formation through reactions in the that generate precursors. Its emissions are regulated under U.S. EPA control rules for ozone non-attainment areas, requiring capture and control in to limit atmospheric releases. Waste management for cyclohexanone involves absorption of spills using inert materials like or , followed by containment and disposal as . containing the compound is typically treated via biological processes in systems, leveraging its ready biodegradability, or by in facilities equipped with afterburners and to ensure complete mineralization. Under the EU REACH regulation, cyclohexanone undergoes monitoring for potential persistent, bioaccumulative, and toxic (PBT) properties, but assessments conclude it meets none of these criteria due to its rapid degradation, low , and moderate ecotoxicity. Global industrial releases, primarily from production and use in manufacturing, are estimated in the range of thousands of tons annually and are subject to environmental reporting to mitigate broader ecological impacts.

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