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EC number: 232-029-1 | CAS number: 7783-82-6
- 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
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The EU RAR contains a review and summary of available data on HF. The studies compiled in this report were assessed as part of the EU RAR and are therefore considered to be suitably reliable. The same test was reviewed and assessed in a SCIENCE REPORT by the UK Environment Agency and also considered as reliable. Test done under GLP conditions. Read across justification is given in section 13 assessment reports: WF6 justification for read across
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 412 (Subacute Inhalation Toxicity: 28-Day Study)
- Principles of method if other than guideline:
- In a range-finding study, groups of five male and five female Fischer 344 rats were exposed to measured concentrations of 0, 1, 10, 25, 65 or 100 ppm (0, 0.83, 8.3, 21, 54 and 83 mg/m3) for 6 hours/day, 5 days/week, for 2 weeks; survivors were sacrificed 2 days later. 10 exposures within 15 days.
- GLP compliance:
- not specified
- Remarks:
- As per EU RAR on HF study reported to be GLP complaint.
- Limit test:
- no
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Route of administration:
- inhalation: gas
- Type of inhalation exposure:
- not specified
- Vehicle:
- air
- Analytical verification of doses or concentrations:
- yes
- Duration of treatment / exposure:
- 6 hours
- Frequency of treatment:
- 5 days/week for 2 weeks
- Remarks:
- Doses / Concentrations:
1 ppm (0,83 mg/m³)
Basis:
analytical conc. - Remarks:
- Doses / Concentrations:
10 ppm (8,3 mg/m³)
Basis:
analytical conc. - Remarks:
- Doses / Concentrations:
25 ppm (21 mg/m³)
Basis:
analytical conc. - Remarks:
- Doses / Concentrations:
65 ppm (54 mg/m³)
Basis:
analytical conc. - Remarks:
- Doses / Concentrations:
100 ppm (83 mg/m³)
Basis:
analytical conc. - No. of animals per sex per dose:
- five male and five female
- Control animals:
- yes
- Dose descriptor:
- NOAEL
- Effect level:
- 1 ppm (analytical)
- Based on:
- test mat.
- Sex:
- male/female
- Dose descriptor:
- NOAEL
- Effect level:
- 0.83 mg/m³ air (analytical)
- Based on:
- test mat.
- Sex:
- male/female
- Critical effects observed:
- not specified
- Conclusions:
- NOAEL for HF is 1 ppm which equals 0.17 ppm of WF6 and 2.1 mg/m³ WF6 at 20 °C and 1,013 bar.
- Executive summary:
In a range-finding study, groups of five male and five female Fischer 344 rats were exposed to measured concentrations of 0, 1, 10, 25, 65 or 100 ppm (0, 0.83, 8.3, 21, 54 and 83 mg/m³) for 6 hours/day, 5 days/week, for 2 weeks; survivors were sacrificed 2 days later (Placke et al, 1990). Exposures to 25 ppm (21 mg/m³) and above resulted in deaths of all females, with deaths beginning on the eighth, third, and second day of exposure at the 25, 65, and 100 ppm (21, 54 and 83 mg/m³) concentrations, respectively. Exposures to 65 and 100 ppm (54 and 83 mg/m³) resulted in deaths of all males, with deaths beginning on the third and second day at the 65 and 100 ppm concentrations, respectively. No deaths occurred during the first day of exposure at any concentration, and no deaths occurred at the lower concentrations.
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEC
- 2.1 mg/m³
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Since WF6 is hydrolising rapidly to HF under ambient and physiological conditions, read across to studies on HF and NaF was done. It is turning out that the fluoride anion is inducing adverse effects, while the effect of the sodium kation or proton (Na+ or H+) is negigible. Tungsten oxides are not considered as dangerous/toxic. So, the read across data are the best possible approach to describe the properties of WF6 and its hydrolisation products.
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Most recent study under GLP conditions.
Justification for classification or non-classification
According to the UN Globally Harmonized System of Classification and Labelling of Chemicals (GHS) Part 3 WF6 is already considered to be acute toxic by inhalation: Category 2
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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