Registration Dossier
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Diss Factsheets
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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
Description of key information
Additional information
No bioaccumulation studies obtained from established experimental protocols are available for TFA. The substance is expected to have a low potential for bioaccumulation according to its log Kow of 0.79 at 25°C. However, because of the structural similarity of TFA to acetate, a biochemical intermediate and microbial nutrient, it was suspected that organisms might use the fluorinated compound to synthesize biomolecules such as lipids and acetylated proteins and several non standard experimental studies were conducted on aquatic and terrestrial organisms.
The results indicate a low level of incorporation of TFA by natural microbial communities and thus their potential to serve as a point for TFA to enter into the food web. Overall incorporation of radioactive TFA in aquatic organisms spanning a range of trophic levels (microbial communities, oligochaetes, macroinvertebrates, Callitriche sp., Lemna sp., and Impatiens capensis) was very low (low ppb range for microbial communities and low ppm range for oligochaetes and jewelweed) and TFA was incorporated into their biomolecule fractions so that it was no longer extracted as TFA and thus was metabolically transformed. Finally, radioactive TFA accumulated around ten times by the algal cells from the media is reported in the Toxicity to aquatic algae and cyanobacteria section.Bioaccumulation data in terrestrial organisms are reported in the toxicity to terrestrial plants section. Pines accumulated TFA as a function of concentration applied and the results indicated that atmospheric uptake may not be the dominant pathway of uptake in environmental conditions but rather root uptake. TFA accumulation by the plant Lycopersicon esculentum showed no extensive metabolism and that TFA is transported through the stem and accumulates in the leaves up to final concentrations of 10 to 20 µmol/g ww. A bioconcentration factor (BCF) of 43 after 35 days of exposure of the root in an aqueous medium was measured for the wheat. Sunflower seedlings were exposed to TFA in aquous medium and bioconcentration factor (BCF) of approximately 22 and 5 after 12 days were found in leaf tissue and stem tissue, respectively. Root tissue reached apparent equilibrium after 5 days exposure with a BCF of approximately 3. All tissues showed a decline in TFA residue concentrations on transfer to clean medium with some evidence of depuration.
In conclusion, these results show that TFA does not accumulate significantly in lower aquatic life forms such as bacteria, algae, small invertebrates, oligochaete worms and in some aquatic and terrestrial plants.
Based on the above data, a waiving for testing bioaccumulation is proposed.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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