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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
Phototransformation in air
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in air
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Long path length FTIR-smog chamber techniques were used to determine k(Cl + CF3CF=CH2), k(OH + CF3CF=CH2), and k(O3 + CF3CF=CH2) in 700 Torr of N2, N2/O2, or air diluent at 296 K.
- Specific details on test material used for the study:
- Test material was obtained from commercial sources. No specific details on the test material were provided.
- Light source:
- other: Fluorescent blacklamps
- Key result
- DT50:
- 15 d
- Remarks on result:
- other: Recalculation representing the worst-case, see 'Any other information on results incl. tables'
- DT50:
- 11 d
- Remarks on result:
- other: Original value in the publication
- Key result
- Reaction with:
- OH radicals
- Remarks on result:
- other: Rate constant = 1.05E-12 cm3/molecule/s
- Transformation products:
- not specified
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Based on the parameters determined in this experiment the atmospheric half-life of the test material was determined to be 15 days. The test material was found to have a negligible global warming potential and no significant contribution to radiative forcing of climate change is expected.
- Executive summary:
In this publication, the atmospheric behaviour of CF3CF=CH2 was studied using long path length FTIR-smog chamber techniques. It was observed that CF3CF=CH2 will not undergo photolysis and effective removal by either wet or dry deposition is not expected. Cl atoms in the atmosphere will not be present in sufficient quantities to impact the lifetime of the test material. Loss mechanisms for CF3CF=CH2 are expected to be the reaction with OH and O3. The value of k(OH + CF3CF=CH2) measured can be used to provide an estimate of the lifetime of CF3CF=CH2 in the atmosphere. This lifetime can be calculated using a global weighted-average OH concentration of 1.0E+06 molecules/cm3, which leads to an estimated lifetime of CF3CF=CH2 of 11 days with respect to reaction with OH radicals, as reported in the publication.
Taking a worst-case scenorio into acount and recalculating the degradation constant in air by using a global annual average OH-radical concentration of 5E-5 molecules/cm3 leads to an estimated lifetime of CF3CF=CH2 with respect to reaction with OH radicals of 15 days. It is concluded that CF3CF=CH2 has a negligible global warming potential and will not make any significant contribution to radiative forcing of climate change.
Reference
DATA TAKEN FROM PUBLICATION
CF3CF=CH2 did not undergo photolysis, therefore it is not expected to be removed effectively by either wet or dry deposition. As no sufficient Cl atoms are present in the atmosphere, the lifetime of CF3CF=CH2 will not be impacted. Loss mechanisms for CF3CF=CH2 are expected to be the reaction with OH and O3. The value of k(OH + CF3CF=CH2) measured can be used to provide an estimate of the lifetime of CF3CF=CH2 in the atmosphere. This lifetime can be calculated using a global weighted-average OH concentration of 1.0E+06 molecules/cm3, which leads to an estimated lifetime of CF3CF=CH2 of 11 days with respect to reaction with OH radicals.
RECALCULATION
Recalculation is based on the R.16 guidance. By relating kOH to the average OH-radical concentration in the atmosphere, the pseudo-first order rate constant in air is determined:
kdegair = kOH x OHCONCAIR x 24 x 3600 (Equation R.16-12)
In this case KOH = 1.05E-12 cm3/molecule/s
OHCONCair = 5E+05 molecule/cm3
kdeg air = 1.05E-12 cm3/molecule/s x 5E+05 molecule/cm3 x 24 x 3600 = 4.54E-02 per day
The resulting DT50 = LN(2)/kdeg air = 1.53E+01 days
Description of key information
Based on the parameters reported in Nielsen et al. (2007), a DT50 of 15 days in air was determined.
Key value for chemical safety assessment
- Half-life in air:
- 15 d
- Degradation rate constant with OH radicals:
- 0 cm³ molecule-1 s-1
Additional information
In this publication, the atmospheric behaviour of CF3CF=CH2 was studied using long path length FTIR-smog chamber techniques. It was observed that CF3CF=CH2 will not undergo photolysis and effective removal by either wet or dry deposition is not expected. Cl atoms in the atmosphere will not be present in sufficient quantities to impact the lifetime of the test material. Loss mechanisms for CF3CF=CH2 are expected to be the reaction with OH and O3. The value of k(OH + CF3CF=CH2) measured can be used to provide an estimate of the lifetime of CF3CF=CH2 in the atmosphere. This lifetime can be calculated using a global weighted-average OH concentration of 1.0E+06 molecules/cm3, which leads to an estimated lifetime of CF3CF=CH2 of 11 days with respect to reaction with OH radicals, as reported in the publication.
Taking a worst-case scenorio into acount and recalculating the degradation constant in air by using a global annual average OH-radical concentration of 5E-5 molecules/cm3 leads to an estimated lifetime of CF3CF=CH2 with respect to reaction with OH radicals of 15 days. It is concluded that CF3CF=CH2 has a negligible global warming potential and will not make any significant contribution to radiative forcing of climate change.
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