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In , an amine oxide, also known as an amine N-oxide or simply N-oxide, is a chemical compound that has the . It contains a - coordinate covalent bond with three additional hydrogen and/or -groups attached to nitrogen. Sometimes it is written as or, alternatively, as .

In the strict sense, the term amine oxide applies only to of tertiary . Sometimes it is also used for the analogous derivatives of primary and secondary amines.

Commonly, amine oxides are white, water-soluble solids:


Applications
Long-chain amine oxides are used as and stabilizers.

Amine oxides are surfactants commonly used in consumer products such as shampoos, conditioners, detergents, and hard surface cleaners. Alkyl dimethyl amine oxide (chain lengths C10–C16) is the most commercially used amine oxide. They are considered a high production volume class of compounds in more than one member country of the Organisation for Economic Co-operation and Development (); with annual production over in the US, Europe, and Japan, respectively. In North America, more than 95% of amine oxides are used in home cleaning products. They serve as stabilizers, thickeners, emollients, emulsifiers, and conditioners with active concentrations in the range of 0.1–10%. The remainder (< 5%) is used in personal care, institutional, commercial products and for unique patented uses such as photography.


Properties
Amine oxides are highly and have a polarity close to that of quaternary ammonium salts. Small amine oxides are very and have an excellent water and a very poor solubility in most organic .

Amine oxides are weak bases with a p Kb of around 4.5 that form , , upon at a pH below their p Kb.

Formation of amine oxides can also be an unwanted process, such as the oxidation of amine-based reagents. Amines left exposed to air can undergo oxidation from atmospheric oxygen, slowly reacting with oxygen to form N-oxides. This process can cause the amines to turn a yellowish color and the N-oxides can decompose further into byproducts. Oxidation due to air can be prevented by storing reagents under inert atmosphere.


Synthesis
Almost all amine oxides are prepared by the of either tertiary aliphatic amines or aromatic N-. Hydrogen peroxide is the most common reagent both industrially and in academia, however are also important. More specialised oxidising agents can see niche use, for instance Caro's acid or mCPBA. Spontaneous or catalysed reactions using molecular oxygen are rare. Certain other reactions will also produce amine oxides, such as the , however they are rarely employed.


Reactions
Amine oxides exhibit many kinds of reactions.
  • Pyrolytic elimination. Amine oxides, when heated to 150–200 °C undergo a to form a hydroxylamine and an . The reaction requires the alkyl groups to have hydrogens at the beta-carbon (i.e. works with ethyl and above, but not methyl)
  • Reduction to amines. Amine oxides are readily converted to the parent amine by common including lithium aluminium hydride, sodium borohydride, catalytic reduction, / , and iron / acetic acid. Pyridine N-oxides can be deoxygenated by phosphorus oxychloride
  • Sacrificial catalysis. Oxidants can be regenerated by reduction of N-oxides, as in the case of regeneration of by N-methylmorpholine N-oxide in the Upjohn dihydroxylation.
  • O-Alkylation. Pyridine N-oxides react with to the O-alkylated product
  • Bis- ter-pyridine derivatives adsorbed on silver surfaces are discussed to react with oxygen to bis- ter-pyridine N-oxide. This reaction can be followed by video-scanning tunneling microscopy with sub-molecular resolution.
  • In the Meisenheimer rearrangement, certain N-oxides rearrange to
  • In the , a tertiary N-oxide is cleaved by acetic acid anhydride to the corresponding and :
    (1990). 9780471264187
    (2025). 9780124297852, Elsevier Science.


Metabolites
Amine oxides are common of medication and psychoactive drugs. Examples include , , and .

Amine oxides of have been developed as that are metabolized in the -deficient cancer tissue to the active drug.


Human safety
Amine oxides (AO) are not known to be carcinogens, dermal sensitizers, or reproductive toxicants. They are readily metabolized and excreted if ingested. Chronic ingestion by rabbits found lower body weight, diarrhea, and lenticular opacities at a lowest observed adverse effect levels (LOAEL) in the range of 87–150 mg AO/kw bw/day. Tests of human skin exposure have found that after 8 hours less than 1% is absorbed into the body. Eye irritation due to amine oxides and other surfactants is moderate and temporary with no lasting effects.


Environmental safety
Amine oxides with an average chain length of 12.6 have been measured to be water-soluble at ~410 g/L. They are considered to have low potential in aquatic species based on log Kow data from chain lengths less than C14 (bioconcentration factor < 87%). Levels of AO in untreated influent were found to be 2.3–27.8 ug/L, while in effluent they were found to be 0.4–2.91 ug/L. The highest effluent concentrations were found in oxidation ditch and trickling filter treatment plants. On average, over 96% removal has been found with secondary activated sludge treatment. Acute toxicity in fish, as indicated by 96h LC50 tests, is in the range of 1,000–3,000 ug/L for carbon chain lengths less than C14. LC50 values for chain lengths greater than C14 range from 600 to 1400 ug/L. Chronic toxicity data for fish is 420 ug/L. When normalized to C12.9, the NOEC is 310 ug/L for growth and hatchability.


See also


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