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EC number: 238-485-8 | CAS number: 14484-69-6
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
No aquatic toxicity tests are available for potassium tetrafluoroaluminate. The results from the structural analogue multiconstituent aluminium potassium fluoride are used instead (for details see Reporting Format as attached to the respective IUCLID entry and CSR Appendix B.3). Reliable GLP compliant aquatic acute ecotoxicity test results for the structural analogue multiconstituent aluminium potassium fluoride are available for fish, invertebrates and algae. As the contents of fluoride, expressed as a percentage of the molar weight in both substances are comparable, namely 53.5% for potassium tetrafluoroaluminate and ca. 51% for multiconstituent aluminium potassium fluoride, as a result no safety factor is applied. Instead, the effect concentrations will be corrected for molecular weight.
An OECD 203 study reported a 96-h LC50 for Brachydanio rerio of >10 mg/L (Solvay Pharmaceuticals, 2010a). The molecular weight corrected effect concentration for potassium tetrafluoroaluminate is 8.9 mg/L, which corresponds to an effect concentration of >4.75 mg fluoride/L.
An OECD 202 study showed that the 48-h EC50 for Daphnia magna is 22.8 mg/L (Solvay Pharmaceuticals, 1999). The molecular weight corrected effect concentration for potassium tetrafluoroaluminate is 20.2 mg/L, which corresponds to an effect concentration of 10.8 mg fluoride/L.
Two reliable OECD 201 studies with Nocolok Flux and Hot melt PAF (both multiconstituent aluminium potassium fluoride) report 72 -h EC50 values for growth rate of 33.5 and 12.7 mg/L, respectively. The 72 hr NOErC values were reported to be 11.2 and 4.3 mg/L, respectively. The lowest observed values, i.e. the ErC50 of 12.7 mg/L and NOErC of 4.3 mg/L will be used in the assessment. The molecular weight corrected effect concentrations for potassium tetrafluoroaluminate are ErC50 = 11.3 mg/L and NOErC = 3.8 mg/L, which corresponds to ErC50 and NOErC values of 6.0 mg fluoride/L and 2.0 mg fluoride/L, respectively.
One GLP-compliant OECD 209 guideline study is available on the toxicity to microorganisms for the structural analogue multiconstituent aluminium potassium fluoride. The 3-h EC50 is >75 mg/L in activated sludge (Solvay Pharmaceuticals, 2010c). The molecular weight corrected effect concentration for potassium tetrafluoroaluminate is >67 mg/L, which corresponds to an effect concentration of >36 mg fluoride/L.
Studies with sediment organisms for potassium tetrafluoroaluminate or any of its structural analogues are not available.
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