Trifluoroacetic acid (TFA) is an organofluorine compound with the chemical formula CF3CO2H. It belongs to the subclass of per- and polyfluoroalkyl substances (PFASs) known as ultrashort-chain perfluoroalkyl acids (PFAAs). TFA, which is only produced industrially, is commonly used in organic chemistry. In the form of its conjugate base trifluoroacetate, it is the most abundant PFAS found in the environment. It is a haloacetic acid, with all three of the acetyl group's hydrogen atoms replaced by fluorine. It is a colorless liquid with a vinegar-like odor. TFA is a stronger acid than acetic acid is, having an acid ionisation constant, Ka, that is approximately 50000 times higher, as the highly electronegative fluorine atoms and consequent electron-withdrawing nature of the trifluoromethyl group weakens the oxygen–hydrogen bond (allowing for greater acidity) and stabilises the anionic conjugate base.
History In 1922, Frédéric Swarts synthesised trifluoroacetic acid, or rather its sodium salt, and investigated its physicochemical properties.
Formation TFA is prepared industrially by the electrofluorination of acetyl chloride or acetic anhydride, followed by hydrolysis of the resulting trifluoroacetyl fluoride:
CH3COCl + 4 HF → CF3COF + 3 H2 + HCl CF3COF + H2O → CF3COOH + HF Wet samples can be dried by addition of trifluoroacetic anhydride. An older route to TFA proceeds via the oxidation of 1,1,1-trifluoro-2,3,3-trichloropropene with potassium permanganate. The trifluorotrichloropropene can be prepared by Swarts fluorination of hexachloropropene.
Via biodegradation of trifluomethyl compounds Trifluoroacetic acid is not produced biologically, but it is a breakdown product of various organofluorine compounds, e.g., the volatile anesthetic agent halothane. It also may be formed by hydroxyl radical-initiated atmospheric oxidation of the commonly used refrigerant 1,1,1,2-tetrafluoroethane (R-134a). Moreover, it is formed as an atmospheric degradation product of almost all fourth-generation synthetic refrigerants, also called hydrofluoroolefins (HFO), such as 2,3,3,3-tetrafluoropropene. Trifluoroacetic acid is also formed by the degradation of some pesticides that contain a trifluoromethyl group (-CF3), such as flufenacet. The German Environment Agency estimated that pesticide use releases approximately 500 metric tonnes of TFA annually in Germany alone, while refrigerants account for around 1170 metric tonnes per year.
Reactions Having a pKa value of around 0, TFA does not exist as such at concentrations found in natural waters. Instead TFA converts to trifluoroacetate, concomitant with the protonation of water. It protonates several weakly basic anions, e.g. azide to give hydrazoic acid.
TFA is the precursor to trifluoroacetic anhydride, trifluoroperacetic acid, and 2,2,2-trifluoroethanol. It is a reagent used in organic synthesis because of a combination of convenient properties: volatility, solubility in organic solvents, and its strength as an acid. TFA is also less oxidizing than sulfuric acid but more readily available in anhydrous form than many other acids. One complication to its use is that TFA forms an azeotrope with water (b. p. 105 °C). TFA is used as a strong acid to remove protecting groups such as Boc used in organic chemistry and peptide synthesis. At a low concentration, TFA is used as an ion pairing agent in liquid chromatography (HPLC) of organic compounds, particularly peptides and small proteins. TFA is a versatile solvent for NMR spectroscopy (for materials stable in acid). It is also used as a calibrant in mass spectrometry. TFA is used to produce trifluoroacetate salts.
Health effects Trifluoroacetic acid is a strong acid. TFA is harmful when inhaled, causes severe skin burns and is toxic for aquatic organisms even at low concentrations. Skin burns are severe, heal poorly and can be necrotic. Vapour fumes have an LC50 of 10.01 mg/L, tested on rats over 4 hours. Inhalation symptoms include mucus irritation, coughing, shortness of breath and possible formation of oedemas in the respiratory tract. Exposure damages the kidneys. TFA is also thought to be responsible for halothane-induced hepatitis. In 2024, the German Federal Institute for Risk Assessment (BfR) formally requested that the European Chemicals Agency (ECHA) reclassify TFA as "presumed" toxic to human reproduction, based on studies showing damage to animal fetuses. In June 2026, ECHA's Risk Assessment Committee (RAC) concluded that TFA fulfils the criteria for toxic to the reproduction class 1B, persistent, mobile and toxic (PMT) as well as very persistent and very mobile (vPvM). In July 2026, the European Food Safety Authority (EFSA) reduced the acceptable daily intake for TFA by 72%, from 0.05 mg/kg body weight/day down to 0.014. It also set the acute reference dose (ARfD) to 0.07 mg/kg body weight. These reductions were based on an assessment of new evidence, including changes in levels of the hormone thyroxine.
Environmental impacts Trifluoroacetic acid is mildly phytotoxic. Uncertainties remain in our understanding of the potential impacts on the environment of TFA. A debate is ongoing regarding its ecological risk due to its persistence, ubiquity in the environment and increasing concentrations globally. TFA exposure is widespread and increasing and it is the most abundant PFAS found in the environment. TFA does not have well-established health advisories or regulatory limits as other PFAAs. Trifluoroacetic acid is also formed by the degradation of pesticides that contain a trifluoromethyl group (-CF3), such as flufenacet. Pesticides have been identified as the main source of TFA in water in agricultural areas. Trifluoroacetic acid degrades very slowly in the environment and has been found in increasing amounts as a contaminant in water, soil, food, and the human body. Median concentrations of a few micrograms per liter have been found in beer and tea. Seawater can contain about 200 ng of TFA per liter. Biotransformation by decarboxylation to fluoroform has been discussed. In October 2024, a publication proposed classifying TFA as a planetary boundary threat, similar to how CFCs are treated.
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