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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 203-933-3 | CAS number: 112-07-2
- 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:
- 133 mg/m³
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:
- DNEL (Derived No Effect Level)
- Value:
- 333 mg/m³
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 169 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- other: See justification and comments below
- Overall assessment factor (AF):
- 1.2
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 203 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- Based on a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- No factor is used for study length as the data shows that the severity of key haemotoxic effect does not increase from 90 days to lifetime exposure (see information on repeat dose oral NTP studies in chapter 7.5.3 of IUCLID dossier)
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rat to human extrapolation.
- AF for other interspecies differences:
- 0.1
- Justification:
- An interspecies toxicodynamic factor is 0.1 is applied based on the much lower sensitivity of humans to haemotoxicity compared to rodents (see section 7.9.3 of IUCLID dossier).
- AF for intraspecies differences:
- 3
- Justification:
- Proposed factor for workers. See detailed justification in document attached to this record.
- AF for the quality of the whole database:
- 1
- Justification:
- default
- AF for remaining uncertainties:
- 1
- Justification:
- default
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 120 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: See justification and comments below
- Overall assessment factor (AF):
- 9
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 1 080 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Assuming 50% absorption the oral NOAEL translates to a dermal NOAEL of 1080mg/kg.
- AF for dose response relationship:
- 3
- Justification:
- Extrapolation from a LOAEL to a NOAEL. Default factor
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Human data
- AF for other interspecies differences:
- 1
- Justification:
- Human data
- AF for intraspecies differences:
- 3
- Justification:
- Proposed factor for workers. See detailed justification in document attached to this record.
- AF for the quality of the whole database:
- 1
- Justification:
- default
- AF for remaining uncertainties:
- 1
- Justification:
- default
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
- Dose descriptor:
- other: NOAEL
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:
- 80 mg/m³
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:
- DNEL (Derived No Effect Level)
- Value:
- 200 mg/m³
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 102 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- other: See justification and comments below
- Overall assessment factor (AF):
- 2
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 203 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- Based on a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- No factor is used for study length as the data shows that the severity of key haemotoxic effect does not increase from 90 days to lifetime exposure (see information on repeat dose oral NTP studies in chapter 7.5.3 of IUCLID dossier)
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rat to human extrapolation.
- AF for other interspecies differences:
- 0.1
- Justification:
- An interspecies toxicodynamic factor is 0.1 is applied based on the much lower sensitivity of humans to haemotoxicity compared to rodents (see section 7.9.3 of IUCLID dossier).
- AF for intraspecies differences:
- 5
- Justification:
- Proposed factor for general population. See detailed justification in document attached to this record.
- AF for the quality of the whole database:
- 1
- Justification:
- default
- AF for remaining uncertainties:
- 1
- Justification:
- default
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 72 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: See justification and comments below.
- Overall assessment factor (AF):
- 15
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 080 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Assuming 50% absorption the oral NOAEL translates to a dermal NOAEL of 1080mg/kg.
- AF for dose response relationship:
- 3
- Justification:
- Extrapolation from a LOAEL to a NOAEL. Default factor
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Human data
- AF for other interspecies differences:
- 1
- Justification:
- Human data
- AF for intraspecies differences:
- 5
- Justification:
- Proposed factor for general population. See detailed justification in document attached to this record.
- AF for the quality of the whole database:
- 1
- Justification:
- default
- AF for remaining uncertainties:
- 1
- Justification:
- default
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:
- 8.6 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: See justification and comments below
- Overall assessment factor (AF):
- 1.5
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 12.9 mg/kg bw/day
- AF for dose response relationship:
- 3
- Justification:
- LOAEL to NOAEL default factor
- AF for differences in duration of exposure:
- 1
- Justification:
- No factor is used for study length as the data shows that the severity of key haemotoxic effect does not increase from 90 days to lifetime exposure (see information on repeat dose oral NTP studies in chapter 7.5.3 of IUCLID dossier)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- LOAEL is a factor derived for humans by PBPK modelling so no additional allometric factor required.
- AF for other interspecies differences:
- 0.1
- Justification:
- An interspecies toxicodynamic factor is 0.1 is applied based on the much lower sensitivity of humans to haemotoxicity compared to rodents (see section 7.9.3 of IUCLID dossier).
- AF for intraspecies differences:
- 5
- AF for the quality of the whole database:
- 1
- Justification:
- default
- AF for remaining uncertainties:
- 1
- Justification:
- default
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 36 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
DNEL related information
- DNEL derivation method:
- other: See justification and comments below.
- Overall assessment factor (AF):
- 15
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 540 mg/kg bw/day
- AF for dose response relationship:
- 3
- Justification:
- LOAEL to NOAEL extrapolation
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Human data
- AF for other interspecies differences:
- 1
- Justification:
- Human data
- AF for intraspecies differences:
- 5
- Justification:
- Proposed factor for general population. See detailed justification in document attached to this record.
- AF for the quality of the whole database:
- 1
- Justification:
- default
- AF for remaining uncertainties:
- 1
- Justification:
- default
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.