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EC number: 471-480-0 | CAS number: 1645-83-6
- 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:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
- Objective of study:
- metabolism
- Principles of method if other than guideline:
- The biotransformation of HFO-1234ze following inhalation exposure was evaluated by determining urinary metabolites excreted for up to 48 hours following exposure.
- GLP compliance:
- yes
Test material
- Reference substance name:
- -
- EC Number:
- 471-480-0
- EC Name:
- -
- Cas Number:
- 1645-83-6
- Molecular formula:
- Hill formula: C3H2F4 CAS formula: C3H2F4
- IUPAC Name:
- (1E)-1,3,3,3-tetrafluoroprop-1-ene
Constituent 1
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 HFO-1234ze in a dynamic exposure chamber consisting of a 20.6-L desiccator, a stirrer and connections to compressed air and a cylinder of HFO-1234ze fitted with flow meters. Metered amounts of HFO-1234ze were mixed with air and introduced into the exposure chamber. Chamber concentrations of HFO-1234ze were monitored at 15-min intervals by taking samples (100 µL) of the chamber atmosphere with a gastight syringe. The content of HFO-1234ze in these samples was determined by GC/MS. - Duration and frequency of treatment / exposure:
- acute 6 hour exposure
Doses / concentrationsopen allclose all
- Dose / conc.:
- 2 000 ppm
- Dose / conc.:
- 10 000 ppm
- Dose / conc.:
- 50 000 ppm
- 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 a study on a comparable fluorocarbon (HFO-1234yf)
- 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: not pooled
- Method type(s) for identification: NMR, LC/MS, GC/MS
- Limits of detection and quantification: 1.2 pmol/mL N-acetyl-S-(3,3,3-trifluoro-trans-propenyl)-L-cysteine, 2.9 pmol/mL S-(3,3,3-trifluoro-trans-propenyl)-mercaptolactic acid, 250 pmol/mL of 3,3,3-trifluoropropionic acid
- Tissues and body fluids sampled : urine
- Time and frequency of sampling: every 6 - 12 hours for 48 hours
- From how many animals: 5
- Method type(s) for identification: NMR, LC/MS, GC/MS - Statistics:
- Not described
Results and discussion
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- S-(3,3,3-trifluoro-trans-propenyl)-mercaptolactic acid, S-(3,3,3-Trifluoro-trans-propenyl)-l-cysteine, N-acetyl-S-(3,3,3-trifluoro-trans-propenyl)-l-cysteine and 3,3,3-trifluoropropionic acid
Any other information on results incl. tables
In urine samples of rats exposed to 50,000 ppm HFO-1234ze, the predominant metabolite was S-(3,3,3-trifluoro-trans-propenyl)-mercaptolactic acid and accounted for 66% of all integrated (19)F-NMR signals in urines. No (19)F-NMR signals were found in spectra of rat urine samples collected after inhalation exposure to 2000 or 10,000 ppm HFO-1234ze likely due to insufficient sensitivity.
S-(3,3,3-Trifluoro-trans-propenyl)-l-cysteine, N-acetyl-S-(3,3,3-trifluoro-trans-propenyl)-l-cysteine and 3,3,3-trifluoropropionic acid were also present as metabolites in urine samples of rats.
Quantification of three metabolites in urines of rats was performed, using LC/MS-MS and GC/MS. The quantified amounts of the metabolites excreted with urine in both mice and rats, suggest only a low extent (<1% of dose received) of biotransformation of HFO-1234ze and 95% of all metabolites were excreted within 18 h after the end of the exposures (t(1/2) app. 6 h). The obtained results suggest that HFO-1234ze is likely subjected to an addition-elimination reaction with glutathione and to a CYP 450 mediated epoxidation at low rates.
The very low extent of biotransformation following inhalation to high exposures of HFO-1234ze indicates covalent binding resulting in potential liver toxicity is likely prevented by effecient detoxification by glutathione. These results are consistent with the lack of hepatotoxic in rats following 90 day inhalation exposure to HFO-1234ze (see section 7.5 for details of this study).
Applicant's summary and conclusion
- Conclusions:
- In urine samples of rats exposed to 50000 ppm HFO-1234ze, the predominant metabolite was S-(3,3,3-trifluoro-trans-propenyl)-mercaptolactic acid and accounted for 66 % of all integrated (19)F-NMR signals in urines. S-(3,3,3-Trifluoro-trans-propenyl)-l-cysteine, N-acetyl-S-(3,3,3-trifluoro-trans-propenyl)-l-cysteine and 3,3,3-trifluoropropionic acid were also present as metabolites in urine samples of rats. Quantification of three metabolites in urines of rats was performed, using LC/MS-MS and GC/MS. This quantification suggest only a low extent (<1% of dose received) of biotransformation of HFO-1234ze and 95 % of all metabolites were excreted within 18 h after the end of the exposures (t(1/2) app. 6 h). The main difference between the rat and mice metabolites is the fact the concentration of S-(3,3,3-Trifluoro-trans-propenyl)-mercaptolactic acid attributes to 66 % of the metabolites in rat in comparison to only 8 % in mice. The obtained results suggest that HFO-1234ze is likely subjected to an addition-elimination reaction with glutathione and to a CYP 450 mediated epoxidation at low rates. The very low extent of biotransformation following inhalation to high exposures of HFO-1234ze 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 HFO-1234ze (see section 7.5 for details of this study).
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