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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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Not specified
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Principles of method if other than guideline:
- No guideline followed. Report details overview of aerobic biodegradation for CFC products overall.
- 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) - Oxygen conditions:
- not specified
- Inoculum or test system:
- not specified
- Details on inoculum:
- Not specified
- Details on study design:
- Not specified
- Reference substance:
- not specified
- Parameter:
- not specified
- Value:
- 0
- Remarks on result:
- other: Dichlorodifluoromethane introduced into aqueous systems will most likely volatize to the atmosphere. Once in the troposphere, dichlorodifluoromethane remains stable.
- Details on results:
- Not specified
- Results with reference substance:
- Not specified
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- 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. No evidence was found for significant biodegradation.
It has been observed in laboratory experiments with contaminated soil-samples that CFCs are slowly biodegradable in anaerobic aquatic environments. Nevertheless, these compounds are persistent in the environment because of their chemical stability.
The “Handbook on Biodegradation and Biological Treatment of Hazardous Organic Compounds By M.H. van Agteren, Sytze Keuning, D. Janssen”states that the biological degradation of chlorofluorocarbons has not been studied extensively. In general, the order of reactivity of reactions in which the carbon-halogen bond is involved is C-I > C-Br > C-CI > C-F. Lesser halogenated aliphatics are more susceptible to hydrolysis and aerobic degradation , while higher halogenated aliphatics are more susceptible to reductive dehalogenation. Therefore, it is not surprising that the substance CFC-12 is very persistent under aerobic conditions. as has been observed in several biological studies, for example with Methylosinus trichosporium strain OB3b.
Reference
No information was found pertaining to the biodegradability of dichlorodifluoromethane. According to Howard et al. (1975) the volatility of dichlorodifluoromethane, as well as other fluorocarbons, would limit, if not preclude, biodegradation. Su and Goldberg (1976), however, report that dichlorodifluoromethane, as well as other synthetic organic compounds, is persistent in natural waters.
Description of key information
Key value taken from published data.
No evidence was found for significant biodegradation.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
Volatility probably precludes biodegradation. It has been observed in laboratory experiments with contaminated soil-samples that CFCs are slowly biodegradable in anaerobic aquatic environments. Nevertheless, these compounds are persistent in the environment because of their chemical stability.
The “Handbook on Biodegradation and Biological Treatment of Hazardous Organic Compounds By M.H. van Agteren, Sytze Keuning, D. Janssen” states that the biological degradation of chlorofluorocarbons has not been studied extensively. In general, the order of reactivity of reactions in which the carbon-halogen bond is involved is C-I > C-Br > C-CI > C-F. Lesser halogenated aliphatics are more susceptible to hydrolysis and aerobic degradation , while higher halogenated aliphatics are more susceptible to reductive dehalogenation. Therefore, it is not surprising that the substance CFC-12 is very persistent under aerobic conditions. as has been observed in several biological studies, for example with Methylosinus trichosporium strain OB3b.
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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