Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 266-096-3 | CAS number: 66063-05-6
- 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:
- 1.6 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 12.5
- Dose descriptor starting point:
- NOAEL
- Value:
- 18 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 20 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The starting point from an oral study (oral NOAEL) is modified taking into account activity levels (*6.7/10), breathing rate (*1/0.38), the extent of oral absorption (46%, measured) and the extent of inhalation absorption (100%, assumed), and differerences in exposure pattern (*7/5). The modified starting point (inhalation NOAEC) is therefore 20 mg/m3.
- AF for dose response relationship:
- 1
- Justification:
- An AF of 1 is used as the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- An AF of 1 is used as the starting point is from a chronic study.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- An AF is not required as allometric factors have already been taken into account when deriving the modified starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- A default AF of 2.5 is used, in line with ECHA guidance.
- AF for intraspecies differences:
- 5
- Justification:
- A default AF of 5 is used, in line with ECHA guidance.
- AF for the quality of the whole database:
- 1
- Justification:
- An AF of 1 is used as the database is of high quality.
- AF for remaining uncertainties:
- 1
- Justification:
- An AF of 1 is used in the absence of 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
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 116 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Dose descriptor starting point:
- NOAEL
- Value:
- 18 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 5 796 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The starting point from an oral study (oral NOAEL) is modified taking into account the extent of oral absorption (46%, measured) and the extent of dermal absorption (0.2%, measured), and differerences in exposure pattern (*7/5). The modified starting point (dermal NOAEL) is therefore 5796 mg/kg bw/d.
- AF for dose response relationship:
- 1
- Justification:
- An AF of 1 is used as the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- An AF of 1 is used as the starting point is from a chronic study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- An AF of 4 is used as the starting point is from a rat study.
- AF for other interspecies differences:
- 2.5
- Justification:
- A default AF of 2.5 is used, in line with ECHA guidance.
- AF for intraspecies differences:
- 5
- Justification:
- A default AF of 5 is used, in line with ECHA guidance.
- AF for the quality of the whole database:
- 1
- Justification:
- An AF of 1 is used as the database is of high quality.
- AF for remaining uncertainties:
- 1
- Justification:
- An AF of 1 is used in the absence of 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
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.3 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 25
- Dose descriptor starting point:
- NOAEL
- Value:
- 18 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 7.2 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The starting point from an oral study (oral NOAEL) is modified taking into breathing rate (*1/1.15), the extent of oral absorption (46%, measured) and the extent of inhalation absorption (100%, assumed). The modified starting point (inhalation NOAEC) is therefore 7.2 mg/m3.
- AF for dose response relationship:
- 1
- Justification:
- An AF of 1 is used as the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- An AF of 1 is used as the starting point is from a chronic study.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- An AF is not required as allometric factors have already been taken into account when deriving the modified starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- A default AF of 2.5 is used, in line with ECHA guidance.
- AF for intraspecies differences:
- 10
- Justification:
- A default AF of 10 is used, in line with ECHA guidance.
- AF for the quality of the whole database:
- 1
- Justification:
- An AF of 1 is used as the database is of high quality.
- AF for remaining uncertainties:
- 1
- Justification:
- An AF of 1 is used in the absence of 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
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 41 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Dose descriptor starting point:
- NOAEL
- Value:
- 18 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 4 140 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The starting point from an oral study (oral NOAEL) is modified taking into account the extent of oral absorption (46%, measured) and the extent of dermal absorption (0.2%, measured). The modified starting point (dermal NOAEL) is therefore 4140 mg/kg bw/d.
- AF for dose response relationship:
- 1
- Justification:
- An AF of 1 is used as the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- An AF of 1 is used as the starting point is from a chronic study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- An AF of 4 is used as the starting point is from a rat study.
- AF for other interspecies differences:
- 2.5
- Justification:
- A default AF of 2.5 is used, in line with ECHA guidance.
- AF for intraspecies differences:
- 10
- Justification:
- A default AF of 10 is used, in line with ECHA guidance.
- AF for the quality of the whole database:
- 1
- Justification:
- An AF of 1 is used as the database is of high quality.
- AF for remaining uncertainties:
- 1
- Justification:
- An AF of 1 is used in the absence of 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:
- 0.18 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Dose descriptor starting point:
- NOAEL
- Value:
- 18 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 18 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The dose descriptor starting point is from an oral study and does not therefore require modification.
- AF for dose response relationship:
- 1
- Justification:
- An AF of 1 is used as the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- An AF of 1 is used as the starting point is from a chronic study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- An AF of 4 is used as the starting point is from a rat study.
- AF for other interspecies differences:
- 2.5
- Justification:
- A default AF of 2.5 is used, in line with ECHA guidance.
- AF for intraspecies differences:
- 10
- Justification:
- A default AF of 10 is used, in line with ECHA guidance.
- AF for the quality of the whole database:
- 1
- Justification:
- An AF of 1 is used as the database is of high quality.
- AF for remaining uncertainties:
- 1
- Justification:
- An AF of 1 is used in the absence of 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
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
