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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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 5 mg/m³
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 5 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 12
- Dose descriptor:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Workers - Hazard for the eyes
Additional information - workers
-
The study in question is a chronic study so no assessment factor higher than 1 is chosen.
-
Interspecies difference: The default assessment factor for interspecies differences for local effects on the respiratory tract is 2.5 (ECHA Guidance Document R.8 p. 38).
-
Intraspecies difference: The default assessment factor for intraspecies differences for workers is 5 and for general population is 10 (ECHA Guidance Document R.8 p. 38).
-
Inhalable fraction: NOAEC calculated on fine nickel dust (MMAD=1.8μm, GSD=2.4). Ferronickel slags' inhalable dust (<100μm) consists of only about 5% with dust of the granulometry of the tested substance and about 17% of total respirable fraction (<10μm). All dust that was examined in the study had a MMAD <2μm, so it is thought that an adjustment must be made on the DNEL value. Using a conservative approach, a factor of 0.25 will be applied to reach a DNELrespand an additional (conservative) factor of 0.25 will be applied to that in order to reach a DNELinh.
The final DNEL for local effects was determined at around 5.53mg/m3 for respirable dust and around 22mg/m3 for inhalable dust.
The OEL for total respirable dust is 5mg/m3 and that for total inhalable dust is 10mg/m3. They are both lower than the respective DNELs, so these will be the final values.Systemic effects
From the available data the most appropriate choice is the result of NTP, 2006a on subchronic toxicity of nickel oxide.
The descriptor has been corrected according to ECHA Guidance Document R.8 p 27
-
Duration of exposure: The default assessment factor for extrapolation of exposure duration from sub-chronic to chronic exposure is 2 (ECHA Guidance Document R.8 p. 38).
-
Interspecies difference: The default assessment factor for interspecies differences for systemic effects is 2.5 ECHA Guidance Document R.8 p. 38).
-
Intraspecies difference: The default assessment factor for intraspecies differences for workers is 5 and for general population is 10 (ECHA Guidance Document R.8 p. 38).
-
Inhalable fraction: NOAEC calculated on fine nickeloxide dust) mass median aerodynamic diameters ranged from 1.89 to 3.29μm) Ferronickel slags' inhalable dust (<100μm) consists of only about 4.5% with dust of the granulometry of the tested substance and about 17% of total respirable fraction (<10μm). All dust that was examined in the study had a MMAD <2μm, so it is thought that an adjustment must be made on the DNEL value. Using a conservative approach, a factor of 0.25 will be applied to reach a DNELrespand an additional (conservative) factor of 0.25 will be applied to that in order to reach a DNELinh.
The final DNEL for systemic effects was determined at 103mg/m3 for the respirable fraction and 414mg/m3 for the inhalable fraction.
The OEL for total respirable dust is 5mg/m3 and that for total inhalable dust is 10mg/m3. They are lower than the respective DNEL, so these will be the final values.
-
The DNELs that were calculated were for inhalation exposure. Two starting points were chosen, one for local and one for systemic effects.
Local effects
From the available data the most appropriate choice is the result of Oller et al, 2008 on chronic toxicity of nickel metal.
The descriptor has been corrected according to ECHA Guidance Document R.8 p 27.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 50 µg/m³
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
DNEL related information
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 50 µg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 12
- Dose descriptor:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
Acute/short term exposure
- Hazard assessment conclusion:
- no-threshold effect and/or no dose-response information available
DNEL related information
General Population - Hazard for the eyes
Additional information - General Population
-
The study in question is a chronic study so no assessment factor higher than 1 is chosen.
-
Interspecies difference: The default assessment factor for interspecies differences for local effects on the respiratory tract is 2.5 (ECHA Guidance Document R.8 p. 38).
-
Intraspecies difference: The default assessment factor for intraspecies differences for the general population is 10 (ECHA Guidance Document R.8 p. 38).
-
Inhalable fraction: NOAEC calculated on fine nickel dust (MMAD=1.8μm, GSD=2.4). Ferronickel slags' inhalable dust (<100μm) consists of only about 4.5% with dust of the granulometry of the tested substance and about 17% of total respirable fraction (<10μm). All dust that was examined in the study had a MMAD <2μm, so it is thought that an adjustment must be made on the DNEL value. Using a conservative approach, a factor of 0.25 will be applied to reach a DNELrespand an additional (conservative) factor of 0.25 will be applied to reach a DNELinh.
The final DNEL for local effects was determined at around 2.8 mg/m3 for respirable dust and around 11mg/m3 for inhalable dust.
The concentration limit for total dust in the atmosphere is 50μg/m3 which is lower than the respective DNEL, so this will be the final valueSystemic effects
From the available data the most appropriate choice is the result of NTP, 2006a on subchronic toxicity of nickel oxide.
The descriptor has been corrected according to ECHA Guidance Document R.8 p 27
-
Duration of exposure: The default assessment factor for extrapolation of exposure duration from sub-chronic to chronic exposure is 2 (ECHA Guidance Document R.8 p. 38).
-
Interspecies difference: The default assessment factor for interspecies differences for systemic effects is 2.5 ECHA Guidance Document R.8 p. 38).
-
Intraspecies difference: The default assessment factor for intraspecies differences for workers is 5 and for general population is 10 (ECHA Guidance Document R.8 p. 38).
-
Inhalable fraction: NOAEC calculated on fine nickeloxide dust) mass median aerodynamic diameters ranged from 1.89 to 3.29μm) Ferronickel slags' inhalable dust (<100μm) consists of only about 5% with dust of the granulometry of the tested substance and about 17% of total respirable fraction (<10μm). All dust that was examined in the study had a MMAD <2μm, so it is thought that an adjustment must be made on the DNEL value. Using a conservative approach, a factor of 0.25 will be applied to reach a DNELrespand an additional (conservative) factor of 0.25 will be applied to reach a DNELinh.
The final DNEL for systemic effects was determined at 51 mg/m3 for the respirable fraction and 207mg/m3 for the inhalable fraction.
The OEL for total respirable dust is 50μg/m3 which is significantly lower than the respective DNEL, so this will be the final value.
-
The DNELs that were calculated were for inhalation exposure. Two starting points were chosen, one for local and one for systemic effects.
Local effects
From the available data the most appropriate choice is the result of Oller et al, 2008 on chronic toxicity of nickel metal.
The descriptor has been corrected according to ECHA Guidance Document R.8 p 27.
It must be noted however that the potential for dispersion of dust from slags, ferronickel-manufg is low, due to its coarseness, so exposure of local population to airbourne ferronickel slags' dust is unlikely.
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