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Diss Factsheets
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EC number: 468-710-7 | CAS number: 754-12-1
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted at reputable university laboratory under GLP-like conditions, principle investigator well recognized expert on fluorocarbon metabolism, and study published in peer reviewed journal
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 008
Materials and methods
- Objective of study:
- metabolism
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The biotransformation of the test substance following inhalation exposure was evaluated by determining urinary metabolites excreted for up to 48 hours following exposure.
- GLP compliance:
- yes
Test material
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan-Winkelmann, Borchen Germany
- Weight at study initiation: 220-250 g
Administration / exposure
- Route of administration:
- inhalation: gas
- Details on exposure:
- TYPE OF INHALATION EXPOSURE: Nose only
Male rats (n = 5) were exposed to targeted concentrations of 2000, 10000, and 50000 ppm test substance in a dynamic exposure chamber consisting of a 20.6-L desiccator, a stirrer and connections to compressed air and a cylinder of test substance fitted with flow meters. Metered amounts of ttest substance were mixed with air and introduced into the exposure chamber. Chamber concentrations of test substance were monitored at 15-min intervals by taking samples (100 μL) of the chamber atmosphere with a gastight syringe. The content of test substance in these samples was determined by GC/MS. - Duration and frequency of treatment / exposure:
- 6 hours exposure, once.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 2 000 ppm
- Remarks:
- Group 1: Low dose.
- Dose / conc.:
- 10 000 ppm
- Remarks:
- Group 2: Mid dose.
- Dose / conc.:
- 50 000 ppm
- Remarks:
- Group 3: High dose.
- No. of animals per sex per dose / concentration:
- 5
- Control animals:
- no
- Details on study design:
- - Dose selection rationale: doses used were the same as those used for the 13 week and other inhalation toxicity studies.
- Details on dosing and sampling:
- METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: Urine
- Time and frequency of sampling: Every 6 hours for 48 hours
- From how many animals: 5
- Method types for identification: NMR, LC/MS/MS, GC/MS
- Limits of detection and quantification: 2.5 pmol/mL N-acetyl-S-(3,3,3-trifluoro-2-hydroxy-propyl)-L-cysteine
- Statistics:
- Not described
Results and discussion
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Inorganic fluoride, N-acetyl-S-(3,3,3-trifluoro-2-hydroxy-propyl)-Lcysteine
Any other information on results incl. tables
In all rat urine samples, the predominant metabolites were two diastereomers of N-Acetyl-S-(3,3,3-trifluoro-2-hydroxy-propyl)-L-cysteine. In 19F-NMR, the signal intensity of these metabolites represented more than 85% (50000 ppm) of total 19F related signals in the urine samples. Trifluoroacetic acid, 3,3,3-trifluorolactic acid, 3,3,3- trifluoro-1-hydroxyacetone, 3,3,3-trifluoroacetone and 3,3,3-trifluoro-1,2-dihydroxypropane were present as minor metabolites. Quantification of N-Acetyl-S-(3,3,3-trifluoro-2-hydroxypropyl)- L-cysteine by LC/MS-MS showed that most of this metabolite (90%) was excreted within 18 h after the end of exposure (t1/2 app. 6 h). In rats, the recovery of N-Acetyl-S- (3,3,3-trifluoro-2-hydroxy-propyl)-L-cysteine excreted within 48 h in urine was determined as 0.297 ± 0.028, 0.627 ± 0.155, and 2.432 ± 0.864 μmoles at 2000, 10000 and 50000 ppm, respectively suggesting only a low extent ( << 1% dose received) of biotransformation of test substance.
The very low extent of biotransformation following inhalation to high exposures of test substance indicates covalent binding resulting in potential liver toxicity is likely prevented by efficient detoxification by glutathione. These results are consistent with the lack of hepatotoxic in rats following 90 day inhalation exposure to test substance (see section 7.5 for details of this study).
Applicant's summary and conclusion
- Conclusions:
- Evaluation of urinary metabolites from rats exposed to the test substance at exposure levels up to 50000 ppm (233000 mg/m3) showed very low levels of metabolism (<< 1%).
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