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EC number: 244-334-7 | CAS number: 21324-40-3
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
- Endpoint:
- sediment toxicity: long-term
- Type of information:
- other: Information on major hydrolysis product of the registered substance (released rapidly on contact with water/moisture).
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well described report of a comprehensive study, published in a peer-reviewed journal.
- Principles of method if other than guideline:
- Determination of aqueous and sediment-associated fluoride to freshwater benthic organisms of various types.
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Fluoride is a product of the rapid reaction of LiPF6 with water. - Analytical monitoring:
- yes
- Details on sediment and application:
- Sediment taken from Long Point, Lake Erie (routinely used as control sediment in toxicity tests performed by the Canadian National Water Research Institute).
Sodium fluoride was weighed, dissolved in 10 ml dilution water and mixed with wet sediment. This was then mixed with dilution water (water:sediment 4;1 v/v) and allowed to settle before use in testing. - Test organisms (species):
- other: Fish: Pimephales promelas (juveniles). Mayfly larvae: Hexagenia limbata. Midge larvae: Chironomus tentans. Amphipods: Hyalella azteca
- Study type:
- laboratory study
- Test type:
- static
- Water media type:
- freshwater
- Type of sediment:
- natural sediment
- Exposure phase:
- total exposure duration
- Remarks:
- Fish (Pimephales promelas) 21 days. Mayfly larvae (Hexagenia limbata) 21 days. Midge larvae (Chironomus tentans) 10 days. Amphipods (Hyalella azteca) 28 days.
- Hardness:
- Water hardness 160 mg CaCO3/l
- Test temperature:
- 20C
- Details on test conditions:
- Sediment/water test systems established in glass jars
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 5 600 mg/kg sediment dw
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: fluoride concentration
- Basis for effect:
- other: growth and survival
- Remarks on result:
- other: P. promelas
- Duration:
- 21 d
- Dose descriptor:
- other: IC25
- Effect conc.:
- 1 221.3 mg/kg sediment dw
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- other: fluoride concentration
- Basis for effect:
- growth rate
- Remarks:
- (Survival IC25 1652.2 mg/kg sediment dw)
- Remarks on result:
- other: H. limbata
- Duration:
- 10 d
- Dose descriptor:
- other: IC25
- Effect conc.:
- 661.4 mg/kg sediment dw
- Conc. based on:
- other: fluoride concentration
- Basis for effect:
- growth rate
- Remarks on result:
- other: C. tentans
- Duration:
- 28 d
- Dose descriptor:
- other: IC25
- Effect conc.:
- 290.2 mg/kg sediment dw
- Conc. based on:
- other: fluoride concentration
- Basis for effect:
- growth rate
- Remarks:
- (Survival IC25 1114.6 mg/kg sediment dw)
- Remarks on result:
- other: H. azteca
- Conclusions:
- A NOEC value for the most sensitive test species (H. azteca ) can be conservatively calculated as one fifth of the reported IC25 for growth (290.2 mg/kg dw): the thus calculated NOEC of 58 mg F-/kg sediment dw corresponds to an LiPF6 NOEC of 77 mg/kg sediment dw (based on fluoride toxicity following complete F- release).
Reference
H. Azteca proved to be the species most sensitive to fluoride toxicity.
Description of key information
As in surface waters, LiPF6 itself will not be present in freshwater or marine sediments: rather the F-, Li+ and phosphate ions will be present in the unexpected event of significant LiPF6 release. From the reported data on toxicity to mammalian and aquatic organisms, it is clear that fluoride is the most toxic of the degradation products. In a study using spiked sediment with fish, mayfly and midge larvae plus amphipods, a lowest NOEC of 58 mg fluoride/kg dry weight was determined. This corresponds to an LiPF6 NOEC of 77.3 mg/kg sediment dw (based on fluoride toxicity following complete F- release).
Key value for chemical safety assessment
- EC10, LC10 or NOEC for freshwater sediment:
- 77.3 mg/kg sediment dw
Additional information
Metcalfe-Smith et al (2003) investigated the long-term toxicity of freshwater lake sediment spiked with sodium fluoride to sediment-foraging fish (fathead minnow: 21-day exposure), mayfly and midge larvae (21- and 10-day exposure respectively) and amphipods (Hyalella azteca: 28-day exposure). H. azteca proved to be clearly the most sensitive to fluoride, based on both survival (LC50 1,114 mgF-/kg dry weight) and growth (IC25 290.2 mgF-/kg dry weight): while no NOEC value was reported, it is possible to estimate from the data a NOEC value of 58 mgF-/kg dry weight, conservatively calculated as one fifth of the IC25 for growth. This corresponds to an LiPF6 NOEC of 77.3 mg/kg sediment dw (based on fluoride toxicity following complete F- release).
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