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EC number: 231-176-9 | CAS number: 7440-67-7
- 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
Link to relevant study record(s)
Description of key information
Short description of key information on bioaccumulation potential result:
Zr metal and salts are poorly absorbed following oral, respiratory or dermal route.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
- Key value for chemical safety assessment
- Discussion
No bioaccumulation potentiel.
A qualitative judgement on the toxicokinetic behaviour was performed based on physico-chemical characteristics. Zirconium is an inorganic substance and thus some physico-chemical characteristics (like the octanol/water partition coefficient) are not defined.
Zr metal (and salts) are poorly absorbed following oral, respiratory or dermal route. Gastrointestinal absorption of Zr salts is negligible; parenterally, administrated salts were slowly absorbed. Absorption factors of 10% should be proposed for oral, inhalation and dermal absorption, representing default values of what is considered still defendable based on the limited physical/chemical data that can be applied for inorganic substances and following the lowest proposed default dermal absorption factor of 10% based on physical/chemical properties (ECHA, 2008). It is recognised that the actual absorption factors for Zirconium will be much lower. Data on Zirconium dichloride oxide in mouse and rat show oral absorption to be at levels of 0.01 to 0.05% of the administered dose (Delongeas JL et al., 1983).
Following inhalation, the main deposition site of Zr particles is the lung. Then, it could be transported in blood to other tissues like the bones. Following intravenous injection, the few amount of Zr absorbed was mainly distributed in soft organs, including liver, ovaries, lung, pancreas, kidney and thymus gland. The higher concentration was found in the ovaries (maximum 8.5 µg Zr/g tissue) and in the liver (maximum 7.1 µg Zr/g tissue).
The few amount of Zr absorbed seems to be excreted mainly through the faeces and in a lesser extent, via the urinary way (< 1 %). Unabsorbed particles are excreted via the urine. Zr was also found in the milk. It seems able to cross the haemato-encephalic barrier and the placenta, and hence could reach the foetus.
ECHA Endpoint specific guidance, Chapter R.7c; section R.7.12.2.1, Dermal absorption. May 2008
Discussion on bioaccumulation potential result:
Zr metal and salts are poorly absorbed following oral, respiratory or dermal route. Gastrointestinal absorption of Zr salts is negligible; parenterally, administrated salts were slowly absorbed.
Following inhalation, the main deposition site of Zr particles is the lung. Then, it could be transported in blood to other tissues like the bones. Following intravenous injection, Zr was mainly distributed in soft organs, including liver, lung, pancreas, kidney and thymus gland, and adipose tissues. The higher concentration was found in the liver and the muscles.
It seems to be excreted mainly through the faeces and, in a lesser extent, via the urinary way (< 1 %). Zr was also found in the milk. It seems able to cross the haemato-encephalic barrier and the placenta, and hence could reach the foetus.
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