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EC number: 200-929-3 | CAS number: 76-05-1
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
Trifluoroacetic acid (TFA) is rapidly absorbed by oral route, submitted to enterohepatic circulation, distributed in the body (including the placenta) and excreted in the urine and the bile as parent compound
Absorption of TFA may occur after skin contact at non corrosive/irritant concentrations.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Trifluoroacetic acid (TFA) is a dense and fluid liquid, considered as a Volatile Organic Compound (VOC), but also fully miscible in water, where it will exist under its ionised form (see § 4). TFA is not considered as bioaccumulable.
TFA is rapidly absorbed by oral route. Absorption of TFA may occur after skin contact at non corrosive/irritant concentrations, considering both the moderate partition coefficient log Kow (0.79) and its high solubility in the water, together with its molecular mass (114 g/mol). Considered as a VOC, inhalation of TFA vapor may occur at room temperature following by absorption considering the physico-chemical properties described above. After oral exposure, TFA is submitted to enteropatic circulation, then distributed in the body via the blood as ionised form considering its distribution coefficient log D (-0.58) and finally excreted mainly in the urine and in the bile (less extent) as parent compound.
Discussion on bioaccumulation potential result:
Several studies were available which explorated the different endpoint of the toxicokinetics (Weight of evidence approach).
Briefly, the study of Kinoshita et al. (1989) showed that the bile was the major channel of elimination of TFA after an exposure to Halothane by the inhalation route. Furthermore, after an enteral administration of TFA, TFA appeared rapidly in the circulatory blood and a considerable amount of TFA was reabsorbed in the gastrointestinal tract and then excreted into the urine and the bile. Therefore, the most important mechanism of long lasting excretion of TFA after halothane anesthesia seemed to be the enterohepatic circulation of TFA.
In several studies (Ganthous, 1986; Divakaran, 1980; Fraser, 1988; Danielsson, 1984 and Saillenfait, 1996 (see section 7.8.2)) it was demonstrated that TFA passed through the placenta barrier and was therefore found in the amniotic fluid after the exposure to halothane or TFA of the dams by oral or inhalation route. In the case of an halothane exposure, it was highlighted that halothane was mainly metabolised into TFA (the end product of the halothane metabolic pathway) by the maternal metabolic system and then TFA passed throughout the placenta barrier.
Taking into account both the results of the studies and the TFA physico-chemical properties, the following toxicokinetics can be assumed that TFA is rapidly absorbed by oral route. Furthermore, absorption of TFA may occur after skin contact at non corrosive/irritant concentrations, considering both the moderate partition coefficient log Kow (0.79) and its high solubility in the water, together with its molecular mass (114 g/mol). Considered as a VOC (see §4), inhalation of TFA vapor may occur at room temperature following by absorption considering the physico-chemical properties described above. After oral exposure, TFA is :
- submitted to enteropatic circulation,
- distributed in the body via the blood as ionised form considering its distribution coefficient log D (-0.58).
- excreted mainly in the urine and in the bile (less extent) as parent compound.
Discussion on absorption rate:
Absorption of TFA may occur after skin contact at non corrosive/irritant concentrations, considering both the moderate partition coefficient log Kow (0.79) and its high solubility in the water, together with its molecular mass (114 g/mol).
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