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Diss Factsheets
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EC number: 241-034-8 | CAS number: 16961-83-4
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- see read across justification
- Reason / purpose for cross-reference:
- read-across source
- Details on sampling:
- No details on sampling given.
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 32.8 - 60.5 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- not specified
- Remarks on result:
- other: concentration calculated for hexafluorsilicic acid
- Details on results:
- Benthic larvae were very sensitive to the concentration of fluoride ion with EC50 values ranging from 26 to 48 mg F-/L (actual concentration). Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 32.8 to 60.5 mg hexafluorosilicic acid/L.
- Executive summary:
Benthic larvae (Chimarra marginata,Hydropsyche lobata, Hydropsyche bulbifera, Hydropsyche exocellataandHydropsyche pellucidula) collected in Spanish rivers were found to be sensitive to the concentration of fluoride ion with EC50 values ranging from 26 to 48 mg F-/L (actual concentration). These organisms appear more sensitive than D. magna according to the EU RAR for hydrogen fluoride; however this may be a reflection of the fact that the study was performed with soft water.
Benthic larvae were very sensitive to the concentration of fluoride ion with EC50 values ranging from 26 to 48 mg F-/L (actual concentration). Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 32.8 to 60.5 mg hexafluorosilicic acid/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- see read across justification
- Reason / purpose for cross-reference:
- read-across source
- Dose descriptor:
- EC50
- Effect conc.:
- >= 137.3 - 428.4 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Remarks on result:
- other: Freshwater, based on hexafluorsilicic acid
- Dose descriptor:
- EC50
- Effect conc.:
- >= 37.8 - 630 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Remarks on result:
- other: Marine, based on hexafluorsilicic acid
- Executive summary:
The ICD reports EC50 values of 109 -340 mg F-/L for freshwater invertebrates and values of 30 -500 mg F-/L for marine invertebrates.
Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 137.3 - 428.4 and 37.8 -630 mg hexafluorosilicic acid/L for freshwater and marine invertebrates, respectively.
Referenceopen allclose all
The ICD reports EC50 values of 109 -340 mg F-/L for freshwater invertebrates and values of 30 -500 mg F-/L for marine invertebrates.
Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 137.3 - 428.4 and 37.8 -630 mg hexafluorosilicic acid/L for freshwater and marine invertebrates, respectively.
Description of key information
For the risk assessment the following EC50 values will be used:
Freshwater: 32.8 mg/L
Marine: 13.23 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 32.8 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 13.23 mg/L
Additional information
Benthic larvae (Chimarra marginata,Hydropsyche lobata, Hydropsyche bulbifera, Hydropsyche exocellata and Hydropsyche pellucidula) collected in Spanish rivers were found to be sensitive to the concentration of fluoride ion with EC50 values ranging from 26 to 48 mg F-/L (actual concentration). These organisms appear to be more sensitive than D. magna according to the EU RAR for hydrogen fluoride; however this may be a reflection of the fact that the study was performed with soft water.
Benthic larvae were very sensitive to the concentration of fluoride ion with EC50 values ranging from 26 to 48 mg F-/L (actual concentration). Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 32.8 to 60.5 mg hexafluorosilicic acid/L.
In the Klimisch 1 study from Fieser et al. (1986) the acute toxicity of sodium fluoride to Daphnina magna was investigated in a 48 hour static test with a test design similar to the OECD 202. Twenty daphnids (< 24 h) were exposed in 4 replicates per concentration and control at test start. Dose verification was performed at the start and end of the exposure. The results were based on the measured concentration of the fluoride anion (F-). The % immobilization of the daphinds was 0, 0, 10, 15, 80 and 100 % at nominal 0 (control), 100, 158, 251, 316 and 398 mg F-/L. The EC50 was calculated to be 247 mg F-/L. Applying the conversion factor from F- to hexafluorosilicic acid, the concentration corresponds to 311.2 mg hexafluorosilicic acid/L.
In the EU-RAR document, the listed 48h EC50 values for daphnids range from 97 to 270 mg F-/L and were based on nominal concentrations. Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 122.2 to 340.2 mg hexafluorosilicic acid/L.
The ICD reports EC50 values of 109 -340 mg F-/L for freshwater invertebrates and values of 30 - 500 mg F-/L for marine invertebrates. Applying the conversion factor from F- to hexafluorosilicic acid, the concentration range corresponds to 137.3 - 428.4 and 37.8 -630 mg hexafluorosilicic acid/L for freshwater and marine invertebrates, respectively.
Hence, benthic invertebrates were most sensitive freshwater organisms and were hence used for the risk assessment for freshwater as worst case.
For the risk assessment the following EC50 values will be used:
Freshwater: 32.8 mg/L
Marine: 13.23 mg/L
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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