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Diss Factsheets
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EC number: 200-893-9 | CAS number: 75-71-8
- 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 water
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in water
- Type of information:
- other: Data from publications
- Adequacy of study:
- supporting study
- Study period:
- Not specified
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Remarks:
- Review document of publicy available data.
- Study type:
- not specified
- Qualifier:
- no guideline followed
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Molecular weight: 129.91 (Weast 1977)
Melting point: -158°C (Weast 1977)
Boiling point at 760 torr: -29.8°C (Weast 1977)
Vapour pressure at 20°C: 4306 torr (Pearson and McConnell 1975)
Solubility in water at 25°C: 280 mg/l (Pearson and McConnell 1975)
Log octanol/water partition coefficient: 2.16 (Hansch et al. 1975) - Radiolabelling:
- not specified
- Analytical method:
- not specified
- Details on sampling:
- Not specified
- Buffers:
- Not specified
- Light source:
- not specified
- Details on light source:
- not specified
- Type of sensitiser:
- not specified
- Details on test conditions:
- Not specified
- Reference substance:
- not specified
- Dark controls:
- not specified
- Computational methods:
- Not specified
- Parameter:
- not specified
- Transformation products:
- not specified
- Details on results:
- Not specified
- Validity criteria fulfilled:
- yes
- Conclusions:
- Dichlorodifluoromethane introduced into aqueous systems will most likely volatize to the atmosphere. Once in the troposphere, dichlorodifluoromethane remains stable. It eventually diffuses into the stratosphere or is carried back to the earth during the precipitation process. Once in the stratosphere dichlorodifluoromethane is photolyzed by shorter wave-length, higher energy ultraviolet light with the subsequent formation of chlorine atoms.
- Executive summary:
Dichlorodifluoromethane introduced into aqueous systems will most likely volatize to the atmosphere. Once in the troposphere, dichlorodifluoromethane remains stable. It eventually diffuses into the stratosphere or is carried back to the earth during the precipitation process. Once in the stratosphere dichlorodifluoromethane is photolyzed by shorter wave-length, higher energy ultraviolet light with the subsequent formation of chlorine atoms.
Reference
No information was found pertaining specifically to the rate of photolysis of dichlorodifluoromethane in the aquatic environment under ambient conditions. Due to the high vapour pressure of dichlorodifluoromethane, volatilization to the atmosphere is quite rapid. The compound is tropospherically stable (Environment Protection Agency 1975; Hanst 1975; Howard and Durkin 1973); it does not react readily with hydroxyl radicals, nor does it photodissociate in the troposphere since it exhibits no absorption of light greater than 200nm (Hanst 1978; Howard et al. 1975). Lovelock at el. (1973) have suggested a tropospheric residence time of 30 years for dichlorodifluoromethane before diffusion to the stratosphere. In the stratosphere, dichlorodifluoromethane is broken down by the absorption of higher energy; shorter wavelength ultraviolet light (Hanst 1978; Rebbert and Ausloos 1975; Jayanty et al 1975). The initial step in photodissociation is the abstraction of the chlorine atom (Environmental Protection Agency 1975): CCl2F2→CClF2+ Cl· . Eventually, the photodissociation proceeds as follows: F2Cl2→·CF2Cl + Cl · →:CF2+ Cl2→: CF2+2Cl· Thus, accoding to Rebbert and Ausloos (1975) the photodissociation of dichlorodifluoromethane results in the release of two chlorine atoms since less energy is required for the cleavage of the C-Cl bond than for the cleavage of the C-F bond. According to Jayanty et al. (1975), the photolysis of dichlorodifluoromethane in the presence of O2at 213.9nm and 25°C leads to the production of CF2O and Cl2and, potentially, chlorine atoms. Chlorine atoms, release by reactions such as these, are theorized to be catalysts in the destruction of the stratospheric ozone layer (Hanst 1978; Environmental Protection Agency 1975).
Description of key information
Key information taken from published data.
Photolysis is probably not significant in aquatic systems; photodissociation
in the stratosphere is the primary fate of this compound.
Key value for chemical safety assessment
Additional information
Dichlorodifluoromethane introduced into aqueous systems will most likely volatize to the atmosphere. Once in the troposphere, dichlorodifluoromethane remains stable. It eventually diffuses into the stratosphere or is carried back to the earth during the precipitation process. Once in the stratosphere dichlorodifluoromethane is photolyzed by shorter wave-length, higher energy ultraviolet light with the subsequent formation of chlorine atoms.
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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