Registration Dossier
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EC number: 700-486-0 | CAS number: 102687-65-0
- 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
Since it is likely that the substance will be absorbed by inhalation and in the absence of substance-specific absorption data for the oral and dermal route, the default absorption values from the REACH guidance (Chapter 8, R.8.4.2) are used for DNEL derivation, namely: 100% for inhalation, 50% for oral and 50% for dermal absorption. Due to the rapid excretion of metabolites formed no bioaccumulation potential is to be expected.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
- Absorption rate - oral (%):
- 50
- Absorption rate - dermal (%):
- 50
- Absorption rate - inhalation (%):
- 100
Additional information
Introduction
The substance is a colorless, liquified gas with a boiling point of 19°C. The substance has a high vapour pressure of 1065 hPa, an octanol/water partition coefficient of 2.2 and the substance is highly soluble in water.
Absorption:
Oral and dermal: Substance-specific absorption data for the oral and dermal route are not available. However, the substance is a gas and therefore dermal and oral exposure is unlikely
Inhalation: The substance has a vapour pressure of 1065 hPa and therefore inhalation is the major route of exposure. Experiments in rats indicated absorption as systemic effects were observed in a 14-day inhalation study at 7500 and 20000 ppm and in a 90-day inhalation study at 10000 and 15000 ppm. Using physiologically based pharmacokinetic (PBPK) modeling techniques, occupational exposure simulation in an adult female human indicated rapid uptake and clearance from blood for the substance with the concentration falling to near zero before the start of a subsequent day's exposure. The blood/air (BA) partition coefficient also indicates absorption. The blood/air partition coefficient in the rat was at least twice as high as in humans. It can therefore be concluded that the substance is likely to be absorbed via the inhalation route.
Metabolism
Metabolism of the substance has been investigated in Sprague Dawley rats, New Zealand rabbits, and in human liver microsomes. S-(3,3,3-trifluoro-trans-propenyl)-glutathione was identified as predominant metabolite of the test substance in rat, rabbit and human liver microsomes in the presence of glutathione. Products of the oxidative biotransformation of the test substance were only minor metabolites when glutathione was present. In rats, both 3,3,3-trifluorolactic acid and N-acetyl-(3,3,3 -trifluoro-trans-propenyl)-L-cysteine were observed as major urinary metabolites. 3,3,3-trifluorolactic acid was not detected in the urine of rabbits exposed the test substance. Several minor metabolites formed by alternative reactions of S-(3,3,3-trifluoro-trans-propenyl)-glutathione were also excreted. Quantitation showed rapid excretion of both metabolites with urine t1/2 of less than 6 hours in both species. Based on metabolite recovery in urine and estimated doses of the test substance received by inhalation, the extent of biotransformation of the test substance was determined as approximately 0.01% of received dose in rabbits and approximately 0.002% in rats. The remaining material is likely exhaled due to its high volatility. The metabolite structures show that the test substance undergoes both oxidative biotransformation and glutathione conjugation at very low rates. The very low extent of biotransformation and the rapid excretion of metabolites formed are consistent with the very low potential for toxicity of the test substance in mammals.
Conclusion
The test substance is absorbed via the inhalation route. The extent of biotransformation is very low and metabolites formed are excreted rapidly. Untransformed test substance is likely exhaled due to the high volatility of the substance. As, moreover, the log P value of the substance is lower than 3, the substance is unlikely to accumulate with the repeated exposure patterns normally encountered in the workplace. In the absence of substance-specific absorption data for the oral and dermal route, the default absorption values from the REACH guidance (Chapter 8, R.8.4.2) are used for DNEL derivation, namely: 100% for inhalation, 50% for oral and 50% for dermal absorptionInformation 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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