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Diss Factsheets
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EC number: 200-839-4 | CAS number: 75-10-5
- 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
Endpoint summary
Administrative data
Description of key information
Aquatic toxicity testing with gases often lead to invalid results because of the technical difficulties associated with the physical state of the substances.
Given the physical nature of difluoromethane and due to the difficulty to test it meaningfully, no experimental aquatic results are available. Instead, QSAR methods were used to estimate the toxicity of the substance to aquatic organisms. The effect concentrations of difluoromethane were estimated using the method described in the EU Technical Guidance Document (2003) and/or the US EPA program ECOSAR (v1.00, 2009). The measured log Kow value of 0.21 was used for the predictions using both QSARs.
Predicted values:
Fish: 96h-LC50 = 1507.037 mg/L
Daphnids: 48h-LC50 = 652.238 mg/L
Green Algae: 96h-EC50 = 142.302 mg/L
All acute toxicity calculations are reliable, validated and fall within the applicability domain of the QSARs. The environmental relevance of these estimations are reinforced with the experimental values obtained for some other members of the category that are presented as supporting studies.
A category approach was used to to support QSAR estimations and reinforce the evidence of low toxicity to aquatic organisms. Commercially available HFCs and HCFCs share common physicochemical and environmental fate. Although it is not possible to identify clear structure-related trends along the series, the common features present in the ecotoxicological profiles of these substances demonstrate that category approach is justified for these two groups of substances. The justification of the category approach is attached to each study record.
Lastly, the exposure of aquatic compartments should be very low based on the volatility of the test substance. In other words, a significant part of the test substance will quickly partition into the atmospheric compartment. In assessment based on QSAR estimations and a category approach, the most conservative values are used to fill the missing endpoints.
Additional information
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.