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EC number: 273-729-7 | CAS number: 69012-29-9 By-product from the production of ferronickel from a complex ore. Consists primarily of oxides of aluminum, iron, magnesium and silicon.
- 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)
Description of key information
Data from a test on toxicity to sediment organisms from waste of slags, ferronickel-manufg. has shown no toxicity up to a load of 1000mg slag/kg sediment. The very low water solubility of Nickel and Chromium in the slags means that it is unlikely to be present in high concentrations and to transport to sediment organisms causing adverse effects. A series of oceanographic studies have not found evidence of toxicity on marine sediment organisms from acute or chronic exposure to ferronickel slags. These studies observe that possible disruption of the ecosystem may occur not due to toxicity towards the organisms but because of bulk quantities that may alter the sediment significantly.
In order to gather more solid evidence regarding the toxicity of the substance, it was attempted to identify possible adverse effects based on data for its recognised constituents, even though the results cannot be applied directly, due to the way the constituents are bound in the matrix of the substance and are not as bioavailable as the free substances that are examined.
There is a number of studies for Nickel sediment toxicity available, but they cannot provide robust information, in order to calculate a relative PNEC value for sediment.
A study on the effects of short-term exposure to Cr(III) in a river sediment has shown no concentration/response correlation (Becker et al). A conservative NOEC that was derived had a value of 1310mg Cr/kg soil dw.
Further study evaluation on long-term effects of slags, ferronickel-manufg. to both freshwater and marine sediment organisms is in progress and will be entered in the dossier as soon as it is finished. If, at the end of the evaluation it is decided that a study needs to be performed, a relevant testing proposal will be submitted to ECHA for approval.
Key value for chemical safety assessment
Additional information
Data from a test on toxicity to sediment organisms from waste of slags, ferronickel-manufg. has shown no toxicity up to a load of 1000mg slag/kg sediment. The very low water solubility of Nickel and Chromium in the slags means that it is unlikely to be present in high concentrations and to transport to sediment organisms causing adverse effects. A series of oceanographic studies have not found evidence of toxicity on marine sediment organisms from acute or chronic exposure to ferronickel slags. These studies observe that possible disruption of the ecosystem may occur not due to toxicity towards the organisms but because of bulk quantities that may alter the sediment significantly.
In order to gather more solid evidence regarding the toxicity of the substance, it was attempted to identify possible adverse effects based on data for its recognised constituents, even though the results cannot be applied directly, due to the way the constituents are bound in the matrix of the substance and are not as bioavailable as the free substances that are examined.
There is a number of studies for Nickel sediment toxicity available, but they cannot provide robust information, in order to calculate a relative PNEC value for sediment.
A study on the effects of short-term exposure to Cr(III) in a river sediment has shown no concentration/response correlation (Becker et al). A conservative NOEC that was derived had a value of 1310mg Cr/kg soil dw.
Further study evaluation on long-term effects of slags, ferronickel-manufg. to both freshwater and marine sediment organisms is in progress and will be entered in the dossier as soon as it is finished. If, at the end of the evaluation it is decided that a study needs to be performed, a relevant testing proposal will be submitted to ECHA for approval.
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