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Bromoacetone

Bromoacetone (CH₃COCH₂Br) is an belonging to the class of α-haloketones, characterized as a volatile, colorless that readily turns upon exposure to air and exhibits a pungent odor. It possesses strong lachrymatory properties, inducing severe irritation to the eyes, upper , and upon contact, rendering it denser than with a around 137 °C. Historically, bromoacetone was deployed as a non-lethal chemical warfare agent during World War I, designated BA by British forces and B-Stoff (white cross) by Germans, exploiting its capacity to incapacitate adversaries through intense lacrimation and respiratory distress without widespread fatalities. Its synthesis typically involves the bromination of acetone in aqueous acetic acid or similar media, facilitating α-substitution due to the enolizable nature of the ketone. Due to its extreme toxicity and the evolution of more effective riot control agents, bromoacetone's wartime and tear gas applications have been obsolete since the mid-20th century, though it retains niche utility in organic synthesis as an alkylating reagent.

History

Discovery and early synthesis

Bromoacetone was first prepared in 1876 by the Russian chemist N. Sokolowsky via the direct bromination of acetone, marking its initial documentation in literature. This synthesis exploited the electrophilic at the alpha position of the , where substitutes a hydrogen on the methyl group adjacent to the carbonyl, yielding CH₃COCH₂Br. The reaction conditions involved treating acetone with , often in the presence of an acid catalyst such as acetic acid to promote formation and subsequent bromination, though early reports emphasized straightforward without specifying stabilizers. Sokolowsky's work, published in Berichte der deutschen chemischen Gesellschaft, described the product as a volatile liquid and noted its incidental irritant effects during handling, consistent with the alkylating reactivity of alpha-haloketones that enables nucleophilic attack by thiols or amines in mucous membranes. Early recognition of bromoacetone as a derivative stemmed from analogous preparations of and iodoacetone in prior decades, with its lachrymatory action emerging from empirical observations in setups rather than targeted irritant studies. These properties were attributed to the compound's ability to form reactive intermediates, underscoring the causal link between alpha-halogen substitution and enhanced electrophilicity in systems.

Deployment in World War I

Germany first deployed bromoacetone in July 1915 as B-Stoff, a lacrimatory agent within the White Cross series of irritants, primarily disseminated via artillery shells such as the T-shell variant. These shells targeted enemy positions to exploit vulnerabilities in respiratory and ocular defenses, with the agent vaporizing upon impact to produce rapid, intense irritation. The compound's effects centered on severe lacrimation, bronchial spasm, and at higher exposures, resulting in temporary incapacitation through blinding tears and violent coughing fits rather than widespread fatalities. Empirical battlefield data indicated low lethality, with most casualties recovering after evacuation, but its psychological and tactical disruption value proved substantial in disrupting advances and holds on the Western Front. British forces referred to bromoacetone as BA gas and encountered it in barrages, while also incorporating similar irritants into their own munitions. It was frequently mixed with () to enhance persistence and diffusion under varying weather conditions, allowing for more reliable area denial compared to standalone applications. By late 1915, bromoacetone's role diminished as shifted to deadlier pulmonary agents like (introduced December 1915) and vesicants such as (1917), which offered greater casualty rates and strategic impact despite bromoacetone's continued limited use in .

Post-war obsolescence

Following the of , 1918, bromoacetone's deployment as a chemical irritant ended abruptly, with halting amid efforts and the destruction of wartime stockpiles. By the early , surplus munitions containing bromoacetone were systematically disposed of, including dumping into the and other sites, as Allied forces cleared battlefields and depots to comply with Versailles Treaty restrictions on German chemical capabilities. This obsolescence was accelerated by the agent's inherent drawbacks: its liquid state, low of 136°C, and tendency to decompose spontaneously, rendering it logistically challenging for storage and dissemination compared to solid alternatives. The 1925 Geneva Protocol further curtailed bromoacetone's prospects by prohibiting the wartime use of "asphyxiating, poisonous or other gases," encompassing irritants like bromoacetone despite their non-lethal classification; while the treaty allowed domestic applications, signatories increasingly favored less toxic options to avoid escalation risks. Interwar experimentation with lacrimators persisted in limited police and military trials, but bromoacetone's superior irritancy—approximately 18 times that of —came at the cost of excessive pulmonary toxicity and skin blistering, prompting replacement by chloroacetophenone (), a crystalline solid with a higher (59°C) that enabled via grenades and sprays with reduced volatility and handling hazards. By , archival evidence from demilitarization programs indicates that remaining bromoacetone reserves had been fully repurposed for industrial synthesis or neutralized, with no documented for active service. Its absence from arsenals underscores the shift toward persistent vesicants and nerve agents for warfare, while CN and later dominated non-lethal roles due to empirical data showing equivalent incapacitation with lower lethality thresholds in field tests. No revival occurred in subsequent conflicts, as bromoacetone's profile failed to meet evolving criteria for efficacy, safety, and treaty compliance.

Chemical Properties

Molecular structure and formula

Bromoacetone, with the systematic IUPAC name 1-bromopropan-2-one, possesses the molecular C₃H₅BrO and a molecular weight of 136.98 g/mol. Its structure consists of a three-carbon backbone featuring a carbonyl group between carbons 1 and 3, with a (CH₃) attached to the carbonyl carbon and a bromomethyl group (CH₂Br) on the adjacent alpha carbon: CH₃C(O)CH₂Br. The bromine atom occupies the alpha position relative to the carbonyl, classifying bromoacetone as an α-haloketone, a shared with analogs such as (CH₃C(O)CH₂Cl), where substitutes for . This positioning lacks a chiral center, precluding optical isomerism, though conformational variations arise from rotation about the C-C bonds adjacent to the carbonyl. The C-Br bond displays polarity arising from the electronegativity differential between carbon (2.55) and (2.96 on the Pauling scale), enhancing the electrophilicity at the alpha carbon. Spectroscopic techniques confirm the functional groups: () spectroscopy reveals the characteristic C=O stretch of the near 1710 cm⁻¹, while () displays signals for the methyl protons around 2.2 ppm, methylene protons shifted downfield due to the adjacent and carbonyl, and the carbonyl carbon in ¹³C NMR.

Physical characteristics

Bromoacetone exists as a clear, colorless to pale yellow at , with a of -37 °C and a ranging from 136 to 137 °C. Its is 1.63 g/cm³ at standard conditions, rendering it denser than . Upon standing, even in the absence of air, the turns and may decompose further into a black resinous mass over extended periods. The compound exhibits poor solubility in water but is soluble in organic solvents such as acetone, , diethyl ether, and . It possesses a pungent and a vapor pressure of 1.1 kPa at 20 °C, reflecting its volatile nature.

Stability and reactivity

Bromoacetone demonstrates inherent instability characteristic of α-halo ketones, decomposing upon standing to yield a black resinous mass via pathways, even in the absence of air. This process is accelerated by exposure to , , or , with the compound rapidly discoloring to and undergoing complete breakdown after several months at in the dark. is a primary degradation mode, contrasting with the relative inertness of non-α-functionalized halogenated solvents, and underscores the electrophilic vulnerability of the α-carbon to self-reaction or environmental nucleophiles. Thermal decomposition or releases and other toxic gases, reflecting cleavage of the C-Br bond under energy input. The compound's oxidative stability is low, as it reacts with strong oxidants, further highlighting the reactivity imparted by the conjugated carbonyl- system that facilitates withdrawal and bond labilization. Due to the electrophilicity of the α-brominated carbon, bromoacetone engages in vigorous with species such as amines and thiols, proceeding via SN2 displacement of bromide to form alkylated products. This heightened reactivity stems from the carbonyl group's activation of the adjacent , enabling facile attack by nucleophilic centers in biological or synthetic contexts. Bromoacetone is also flammable, possessing a of 51 °C, which necessitates cautious handling to avoid ignition under ambient conditions.

Synthesis

Laboratory preparation

Bromoacetone is prepared in the laboratory primarily through the -catalyzed α-bromination of acetone with molecular . The reaction relies on the enolization of acetone in the presence of , followed by electrophilic bromination at the α-position. A standard procedure involves mixing acetone with glacial acetic , then adding dropwise at a controlled of 30–35°C to manage the exothermic nature of the and limit over-bromination to dibromoacetone. For example, 500 mL of acetone, 372 mL of glacial acetic , and 500 mL of are stirred while 800 g of is added over several hours, followed by of the crude product under reduced to yield colorless to pale yellow liquid. Reported yields for this method range from 50–51% of theoretical. An alternative approach uses dissolved in acetone added to an aqueous solution of and at 30–35°C, generating in for bromination. This method also requires for purification and emphasizes ventilation due to irritating vapors. The reaction's exothermicity necessitates cooling baths, and all manipulations should occur in a well-ventilated given the of reagents and product. Purity is verified post-distillation via techniques such as gas chromatography-mass spectrometry (GC-MS) or determination, aiming for >95% to ensure suitability for research applications.

Industrial-scale production

During , Germany produced bromoacetone on an industrial scale for deployment as the lacrimatory agent B-Stoff, necessitating adaptations of laboratory bromination methods to handle large volumes amid wartime resource constraints. The core reaction remained the acid-catalyzed addition of to acetone, conducted in continuous flow reactors to enhance throughput and safety by maintaining steady-state conditions and rapid mixing, which reduced hotspots prone to side reactions. Excess acetone (typically 5-10 equivalents) was employed to suppress polybromination, favoring selective monobromination at the alpha position while the byproduct was continuously neutralized with bases such as to maintain pH and prevent equipment degradation. German processes incorporated electrolytic generation of from in the presence of acetone, enabling bromination without handling elemental bromine separately, which was advantageous given bromine shortages; this electrochemical approach yielded up to 90% under optimized conditions but faced persistent challenges from the acidic, halide-rich environment, requiring specialized lead-lined or reactors. Post-purification involved under reduced pressure to isolate the product, with overall process efficiency prioritized over purity for munitions filling. Contemporary industrial demand for bromoacetone is negligible, confined to trace or specialty chemical needs, where echoes of wartime continuous bromination persist but at microgram-to-gram scales using safer, enclosed flow systems to mitigate hazards; large-scale revival is precluded by superior alternatives for and stringent regulations on toxic haloketones.

Applications

Military and uses

Bromoacetone served as a key lachrymatory agent in German chemical warfare during , designated B-Stoff and incorporated into White Cross (Weißkreuz) mixtures alongside agents like bromobenzyl cyanide. Deployed primarily in shells from mid-1916 onward, it functioned for area denial by inducing intense irritation to the eyes, , and , thereby forcing exposed troops to don gas masks or abandon positions. This non-lethal incapacitation approach minimized enemy fatalities while disrupting defensive lines, with its potency derived from rapid vaporization and dispersal effectiveness even in low concentrations within munitions payloads. Tactical limitations arose from bromoacetone's high , which facilitated quick evaporation but also risked self-contamination of artillery crews through fumes during shell handling and firing, exacerbating operational hazards in windy or confined conditions. Battlefield applications in engagements demonstrated its capacity for widespread temporary disablement, though precise incapacitation metrics varied by environmental factors like and , often resulting in inconsistent coverage and occasional blowback on positions. Post-World War I, bromoacetone underwent limited evaluation for applications due to its irritant properties, but its elevated toxicity profile—capable of causing pulmonary damage beyond mere —rendered it unsuitable for non-combatant dispersal. By the 1930s, it was supplanted by less hazardous alternatives such as chloroacetophenone (), which provided comparable crowd-dispersing efficacy with reduced risk of severe injury.

Role in organic synthesis

Bromoacetone acts as a versatile α-haloketone in , primarily due to the electrophilic bromomethyl group that enables , , and cyclization reactions. The bromide serves as an effective , offering greater selectivity in displacements compared to chloride analogs like , as bromine's intermediate reduces over-alkylation while supporting efficient enolate trapping and α-functionalization. This reactivity positions it as a for constructing carbon-carbon and carbon-heteroatom bonds in complex molecules. In heterocyclic synthesis, bromoacetone condenses with thioureas or thioamides under Hantzsch conditions to form thiazoles, which are scaffolds in pharmaceuticals exhibiting antibacterial and properties. It also reacts with N-aryl- or N-alkylaminomethylenecyanoacetic derivatives in the presence of base to yield 3-aminopyrroles, useful intermediates for pyrrole-based agrochemicals and bioactive compounds. Additional applications include of nitroazoles to produce acetonyl derivatives, facilitating further for energetic materials or heterocycle elaboration. Bromoacetone further supports ring-closing strategies, such as in the of indolizines by refluxing with ethyl 2-methylnicotinate in , yielding 8-ethoxycarbonyl-2-methylindolizine in 30% yield as a precursor for analogs. Its role extends to formal [3+3] annulations via benzotriazolylpropan-2-one intermediates derived from bromoacetone, enabling access to substituted pyridines relevant to . These transformations underscore its utility in targeted syntheses where precise control over α-position reactivity is essential.

Minor and historical applications

Bromoacetone has been examined in historical agricultural trials as a potential fumigant component, including mixtures tested against weevils in stored products, with concentrations up to 1:2000 showing no immediate phytotoxic effects on during short exposures but ultimately abandoned due to its , lachrymatory properties, and risks documented in mid-20th-century studies. In processes involving chlorination of -rich sources, bromoacetone emerges as a minor haloacetone disinfection , with enhancing its formation alongside other volatiles, as noted in analyses paralleling disinfection dynamics. Analytically, bromoacetone appears in standardized protocols like EPA 8260B for detecting volatile organic compounds in solid via , serving as a for halogenated ketones in environmental and matrices rather than a routine detection for halides.

Toxicology and Health Effects

Mechanisms of toxicity

Bromoacetone functions as a potent alkylating agent due to its alpha-bromoketone structure, which enables at the carbon bearing the atom. This reactivity allows it to form covalent bonds with electron-rich sites in biomolecules, particularly sulfhydryl groups (-SH) on residues in proteins. Such disrupts and function, including in enzymes and structural proteins like mucins in ocular and respiratory epithelia, resulting in denaturation and impaired barrier integrity. This covalent modification is the primary biochemical basis for its irritant effects, as alpha-halo ketones like bromoacetone exhibit selective reactivity toward soft nucleophiles such as thiols over harder ones like under physiological conditions. Inhalation of bromoacetone vapor leads to rapid interaction with moist mucosal surfaces, where the compound's electrophilicity drives before significant occurs. While can produce (HBr) and potentially alpha,beta-unsaturated ketones with irritant properties similar to , the dominant toxicity stems from direct protein modification rather than decomposition products alone. The potency is evidenced by sensory thresholds as low as 0.1 in humans and a 4-hour LC50 of 1,390 (4,800 mg/m³) in rats, reflecting efficient local reactivity in peripheral tissues. This mechanism contrasts with nerve agents, which achieve systemic toxicity via irreversible inhibition of through . Bromoacetone induces peripheral sensory disruption via localized -induced and activation, without penetrating to cause central overload or characteristic poisoning symptoms like convulsions. The absence of enzyme-specific targeting beyond limits its effects to surface-level , differentiating it from agents designed for deeper physiological interference.

Acute exposure symptoms

Acute exposure to bromoacetone vapor or liquid primarily manifests as severe to the , , and , with symptoms onset typically within minutes of contact. Ocular effects include intense lacrimation, , burning sensation, redness, and pain; occurs in approximately 30% of subjects at 0.1 for 1 minute and in 100% at 1.0 for the same duration, while corneal damage may result from concentrations exceeding 10 . Skin contact with the liquid causes immediate painful burns, , and vesication upon prolonged exposure, potentially leading to blistering and ulceration. Inhalation triggers upper respiratory irritation, including coughing, , chest tightness, nasal discharge, and ; low concentrations (e.g., 0.1 for 1 minute) can induce discomfort and lacrimation, escalating to gasping, wheezing, and at higher levels such as 28-131 in animal models or wartime exposures around 100 for several minutes. Thresholds for notable effects include a (NOAEL) of 1.0 and lowest-observed-adverse-effect level (LOAEL) of 2.0 in rats for mild respiratory responses like . Historical accounts from deployments as a lachrymator indicate most symptoms, such as irritation and respiratory distress, resolve within 1-2 hours following brief exposure without complications, though higher doses risked delayed .

Chronic and long-term risks

Repeated or chronic of bromoacetone may lead to , characterized by , production, and , based on extrapolations from its irritant properties and limited exposure data. have demonstrated liver and damage at high exposure levels, suggesting potential cumulative from prolonged low-level contact, though human data remain sparse. As an α-halo ketone, bromoacetone exhibits reactivity capable of alkylating DNA bases via SN2 mechanisms, akin to other α-halo carbonyl compounds that form adducts with nucleosides and demonstrate genotoxicity in bacterial assays. This structural feature implies possible mutagenic potential, though direct testing for bromoacetone is absent; predictive models based on reaction mechanisms classify most α-halo carbonyls as mutagenic due to their electrophilic nature. No carcinogenicity studies exist for bromoacetone in animals or humans, and it is not classified by the International Agency for Research on Cancer (IARC), reflecting data deficiencies rather than established safety. Inferences from analogous α-halo ketones suggest elevated long-term cancer risks, but absence of studies precludes definitive assessment; occupational exposure limits are unavailable due to its rarity and historical use.

Safety, Handling, and Environmental Impact

Occupational safety measures

Handling bromoacetone requires strict adherence to , such as performing all manipulations in a chemical to minimize airborne exposure, supplemented by including chemical-resistant gloves, protective clothing, safety goggles, and a full-face with appropriate cartridges for vapors and acid gases. Good hygiene practices, including washing hands thoroughly after handling and prohibiting eating, drinking, or smoking in the work area, further reduce risks. For storage, bromoacetone should be kept in tightly sealed containers in a cool, well-ventilated area away from heat sources, ignition points, strong oxidants, and incompatible materials to prevent decomposition or fire hazards. Containers must be stored locked and separated from food or feedstuffs. In the event of a spill, immediately evacuate non-equipped personnel, ensure ventilation, and eliminate ignition sources before containing the liquid with inert absorbents like sand or vermiculite, transferring to sealed disposal containers for hazardous waste handling; residual areas should be flushed with water. Bromoacetone is classified by the U.S. Department of Transportation as UN 1569, a Poison Inhalation Hazard (Class 6.1 with subsidiary Class 3 flammability), requiring specialized packaging and labeling for transport. No established occupational exposure limits exist, necessitating air monitoring in handling areas to detect vapors below perceptible irritation thresholds.

Environmental persistence and effects

Bromoacetone demonstrates low environmental persistence attributable to its high reactivity as an . In the atmosphere, reaction with hydroxyl radicals yields an estimated of 54 days at typical concentrations. In aqueous systems, photolysis represents a key under sunlit conditions, while —facilitated by nucleophilic attack on the activated methylene carbon—occurs readily, particularly at alkaline , yielding hydroxyacetone as a primary product. This rapid transformation limits long-term accumulation in water bodies, though the compound sinks upon release and dissolves slowly before polymerizing to form violet residues. Despite its transience, bromoacetone exhibits to aquatic organisms at low concentrations, prompting warnings against entry into water intakes due to risks to and . Specific metrics like LC50 values for remain unreported in standard databases, but its irritant and corrosive properties extend to ecosystems, potentially disrupting microbial communities and primary producers in spills. As a CERCLA-designated hazardous substance with a reportable quantity of 1,000 pounds, improper disposal can lead to contamination, where incomplete might allow transient migration before degradation. Bioaccumulation and potentials are negligible, given the 's , rapid aqueous breakdown, and lack of conducive to trophic transfer. Short-term spill effects may involve localized oxygen demand from reactive byproducts or enhanced microbial respiration, but overall recovery aligns with the substance's short half-lives in environmental compartments.

International treaties and prohibitions

The deployment of bromoacetone as a lacrimatory irritant during , particularly by German forces under the designation B-Stoff, underscored the need for international restrictions on such agents, influencing the 1925 for the Prohibition of the Use in War of Asphyxiating, Poisonous or Other Gases, and of Bacteriological Methods of Warfare. This protocol, signed on 17 June 1925 and entering into force on 8 February 1928 for initial parties, explicitly bans the wartime employment of chemical agents like bromoacetone, categorizing them among prohibited gases without distinguishing irritants from lethal toxins at the time. Although the protocol permits reservations allowing retaliatory use and does not preclude applications outside combat, it established a foundational norm against irritant deployment in armed conflict, addressing gaps in prior Conventions of 1899 and 1907 that focused narrowly on gas-diffusing projectiles but omitted liquid or vaporized irritants. The 1993 Convention on the Prohibition of the Development, Production, Stockpiling and Use of Chemical Weapons and on Their Destruction (), entering into force on 29 April 1997, builds on the framework by defining chemical weapons to encompass toxic chemicals and their precursors intended for hostile purposes or warfare methods, excluding purposes like industrial, agricultural, , , or protective applications. Bromoacetone qualifies as a agent under Article II(9)(d), which permits non-lethal chemicals for temporary incapacitation in non-warfare scenarios such as , provided they are not used as a method of warfare; however, it is not enumerated in the 's Schedules 1, 2, or 3 of controlled toxic chemicals or precursors, subjecting it to general verification rather than specific declaration requirements. The Organisation for the Prohibition of Chemical Weapons (OPCW), tasked with implementation, monitors agents through scientific advisory reports and inspection regimes, ensuring compliance with prohibitions on weaponization while allowing civilian formulations. Export controls under the , an informal multilateral regime formed in 1985 to impede chemical weapons , harmonize licensing for dual-use chemicals and that could facilitate of agents like bromoacetone, though the compound itself evades direct listing as a precursor and relies on broader controls over alpha-halogenated ketones and synthesis apparatus. No comprehensive outright exists for bromoacetone in non-military contexts, but its historical irritant role sustains scrutiny under these regimes to prevent diversion to prohibited ends.

National regulations and hazardous substance listings

In the United States, bromoacetone is designated a hazardous substance under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), with a reportable quantity of 1,000 pounds (454 kg) for releases requiring notification to the Response Center. It is regulated under the Toxic Substances Control Act (TSCA) for chemical inventory and risk management, including potential toxicity reporting requirements for manufacturers or importers. The (OSHA) has not established a (PEL) for bromoacetone, though it must be handled under the Hazard Communication Standard (29 CFR 1910.1200) with appropriate labeling, safety data sheets, and worker training due to its irritant and toxic properties. For short-term exposure, guidelines align with irritant thresholds for similar alpha-halo ketones, such as ACGIH's ceiling limit recommendations for compounds like at 1 ppm, emphasizing immediate mitigation of airborne concentrations. The U.S. () classifies bromoacetone as a ( 6.1), Packing Group II, under UN 1569, designating it a poison requiring specific , labeling, and placarding for . In the , bromoacetone is subject to the REACH Regulation (EC) No 1907/2006, where alpha-halo ketones are evaluated for restrictions on uses posing unacceptable risks, particularly in consumer mixtures due to and ; registration and authorization may be required for industrial volumes exceeding 1 tonne per year. It is classified under the Globally Harmonized System (GHS) and as acutely toxic by (Category 2), causing serious eye damage (Category 1), and skin irritation (Category 2), mandating corrosive and toxic pictograms, signal words like "Danger," and statements such as H330 ("Fatal if inhaled") on labels. Many other nations, including , , and , adopt GHS classifications for bromoacetone, requiring similar corrosive and toxic labeling for import, storage, and handling.

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