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EC number: 215-238-2 | CAS number: 1314-61-0
- 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
ACUTE ORAL TOXICITY
The oral toxicity of ditantalum pentaoxide has been recorded in key literature to be LD0 ≥ 8000 mg/kg in rats (Cochran 1950).
ACUTE INHALATION TOXICITY
The acute inhalation toxicity of ditantalum pentaoxide was determined to be LD0 > 3.89 mg/l in the key study Wilcox (2001), according to the following standardised guidelines: OECD 403, EPA OPPTS 870.1300, EEC (Annex II, point 5.2.3) and J-MAFF.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- The key paper of Cochran (1950) provided sufficient information to address this endpoint and was assessed to be reliable with restrictions (2, Klimisch 1997)
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- A reliable Klimisch 1 study is available to address this endpoint, along with 2 supporting studies. The quality of the database is high.
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
ACUTE ORAL TOXICITY
Cochran (1950) showed that the LD₀ of the test material is above the limits of classification. The publication provides data which is of a good standard and was assigned a reliability score of 2 using the principles for assessing data quality as set out in Klimisch (1997). Furthermore the study was cited by O´Neil (2006), Clayton (1981) and Venugopal (1978), which are given as secondary source.
ACUTE INHALATION TOXICITY
The key study (Wilcox, 2001) was conducted in line with GLP and standardized guidelines with a sufficient level of detail to assess the quality of the study. Five male and five female Sprague-Dawley rats were exposed to the test material as an aerosol at the maximum practical concentration for 4 hours. The LD₀ was determined to be >= 3.89 mg/l, as no mortalities were seen at the maximum concentration. The study was performed to a good standard and was assigned a reliability score of 1 using the principles for assessing data quality as set out in Klimisch (1997).
Nemetschek-Gansler (1975) and ACGIH (2001) have been provided as supporting data. They show that no morphological changes occur in the lungs within a realistic exposure level. They have been assigned reliability scores of 2 and 4 respectively, according to Klimisch (1977).
Justification for selection of acute toxicity – oral endpoint
No single study was considered robust enough to be considered as the key study. Therefore a weight of evidence approach was used.
Justification for selection of acute toxicity – inhalation endpoint
Study conducted in accordance with a recognized OECD guideline and in accordance with GLP in a certified laboratory. Study is assigned a reliability score of 1 in accordance with Klimisch (1997).
Justification for selection of acute toxicity – dermal endpoint
Testing via the dermal route was not conduced as the inhalation route was considered a more likely route of exposure.
Justification for classification or non-classification
ACUTE ORAL TOXICITY
The data indicate that exposure to the test material does not result in effects which require classification. Therefore the material does not require classification in line with Regulation (EC) No. 1272/2008 or Directive 67/548/EEC.
ACUTE INHALATION TOXICITY
The data indicate that exposure to the test material does not result in effects which require classification. Therefore the material does not require classification in line with Regulation (EC) No. 1272/2008 or Directive 67/548/EEC.
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