Registration Dossier
Registration Dossier
Diss Factsheets
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EC number: 200-353-2 | CAS number: 57-88-5
- 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:
- 132 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECETOC guidance (Technical Report No. 110, October 2010)
- Overall assessment factor (AF):
- 12
- Modified dose descriptor starting point:
- LOAEC
- Value:
- 1 587 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- according to guidelines; there is no evidence that route-to-route extrapolation cannot be applied.
- AF for dose response relationship:
- 2
- Justification:
- LOAEL based minor effects on liver, which have been demonstrated to be reversible. Comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for differences in duration of exposure:
- 2
- Justification:
- Assuming chronic exposure of the worker; comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- No correction for caloric demand for inhalation.
- AF for other interspecies differences:
- 1
- Justification:
- according to guideline
- AF for intraspecies differences:
- 3
- Justification:
- according to guideline
- AF for the quality of the whole database:
- 1
- Justification:
- whole dataset provides reliable information
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 18 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECETOC guidance (Technical Report No. 110, October 2010)
- Overall assessment factor (AF):
- 84
- Modified dose descriptor starting point:
- other:
- Value:
- 1 500 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- according to guidelines; there is no evidence that route-to-route extrapolation cannot be applied.
- AF for dose response relationship:
- 2
- Justification:
- LOAEL based minor effects on liver, which have been demonstrated to be reversible. Comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for differences in duration of exposure:
- 2
- Justification:
- assuming chronic exposure of the worker; comparable effects were observed both after 4 and 24 weeks of exposure
- AF for interspecies differences (allometric scaling):
- 7
- Justification:
- mice to humans
- AF for other interspecies differences:
- 1
- Justification:
- not relevant
- AF for intraspecies differences:
- 3
- Justification:
- according to guideline (difference in sensitivity among workers)
- AF for the quality of the whole database:
- 1
- Justification:
- whole dataset provides reliable information
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
According to ECHA Guidance R8 (2012), for exposure to dust, the general dust limits of 10 mg/m3for the inhalable airborne fraction and 3 mg/m3for the respirable airborne fraction used in setting Occupational Exposure Limits in many countries should be considered in combination with nature of the dust. For non-soluble inert dusts (such as cholesterol) if the derived DNEL for inhalation is above the dust limits, the general dust limits should apply for exposure scenarios with exposure to dust. For cholesterol the DNELs based on the dataset are above the general dust limit. Consequently, the general dust limit needs to be considered for cholesterol.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 39 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECHA REACH guidance/ ECETOC guidance (Technical Report No. 110, October 2010)
- Overall assessment factor (AF):
- 20
- Modified dose descriptor starting point:
- LOAEC
- Value:
- 783 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- according to guidelines; there is no evidence that route-to-route extrapolation cannot be applied.
- AF for dose response relationship:
- 2
- Justification:
- LOAEL based minor effects on liver, which have been demonstrated to be reversible. Comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for differences in duration of exposure:
- 2
- Justification:
- Assuming chronic exposure of the worker; comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- No correction for caloric demand for inhalation.
- AF for other interspecies differences:
- 1
- Justification:
- according to guidelines
- AF for intraspecies differences:
- 5
- Justification:
- according to guidelines
- AF for the quality of the whole database:
- 1
- Justification:
- whole dataset provides reliable information
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 10.7 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECETOC guidance (Technical Report No. 110, October 2010)
- Overall assessment factor (AF):
- 140
- Modified dose descriptor starting point:
- other:
- Value:
- 1 500 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- according to guidelines; there is no evidence that route-to-route extrapolation cannot be applied.
- AF for dose response relationship:
- 2
- Justification:
- LOAEL based minor effects on liver, which have been demonstrated to be reversible. Comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for differences in duration of exposure:
- 2
- Justification:
- Assuming chronic exposure of the worker; comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for interspecies differences (allometric scaling):
- 7
- Justification:
- mice to humans
- AF for other interspecies differences:
- 1
- Justification:
- according to guideline
- AF for intraspecies differences:
- 5
- Justification:
- according to guideline (difference in sensitivity among the general population)
- AF for the quality of the whole database:
- 1
- Justification:
- whole dataset provides reliable information
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 10.7 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECETOC guidance (Technical Report No. 110, October 2010)
- Overall assessment factor (AF):
- 140
- Modified dose descriptor starting point:
- other: NOAEL
- Value:
- 1 500 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- not applicable, as starting point is oral toxicity study.
- AF for dose response relationship:
- 2
- Justification:
- LOAEL based minor effects on liver, which have been demonstrated to be reversible. Comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for differences in duration of exposure:
- 2
- Justification:
- Assuming chronic exposure of the worker; comparable effects were observed both after 4 and 24 weeks of exposure.
- AF for interspecies differences (allometric scaling):
- 7
- Justification:
- mice to humans
- AF for other interspecies differences:
- 1
- Justification:
- according to guideline
- AF for intraspecies differences:
- 5
- Justification:
- according to guideline
- AF for the quality of the whole database:
- 1
- Justification:
- whole dataset provides reliable information
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
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