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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 283-829-2 | CAS number: 84731-70-4
- 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:
- 49.3 mg/m³
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- 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:
- 1 000 mg/kg bw/day
- Value:
- 1 230 mg/m³
- Explanation for the modification of the dose descriptor starting point:
No inhalatory study available - Oral read across study used for route to route extrapolation
- AF for dose response relationship:
- 1
- Justification:
- Corrected NOEC
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic default
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Route-route concentration, no allometric scaling required
- AF for other interspecies differences:
- 2.5
- Justification:
- Default for interspecies variability - remaining differences in case of no other specific susceptibility differences info available.
- AF for intraspecies differences:
- 5
- Justification:
- Assessment factor for workers
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on target substance
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:
- 14 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- 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:
- 1 000 mg/kg bw/day
- Value:
- 1 400 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
No dermal study available - Oral read across study used for route to route extrapolation
- AF for dose response relationship:
- 1
- Justification:
- Corrected NOEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic default
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value for study animal rats.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default for interspecies variability - remaining differences in case of no other specific susceptibility differences info available.
- AF for intraspecies differences:
- 5
- Justification:
- Worker default
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on target substance
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
Long-term systemic inhalatory NOEC calculated based on the oral repeat dose NOAEL value as described in the guidance R.8 example B.3. The above factors were used to calculate a DNEL of 49.3 mg/m³.
Long-term systemic dermal NOEL calculated based on the oral repeat dose NOAEL value as described in Guidance R.8 . The above factors were used to calculate a DNEL of 14 mg/kg bw/day.
The material is not classified for acute systemic effects, therefore derivation of acute DNEL is not required. Long-term DNELs are considered sufficient to ensure acute effects do not occur.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 8.7 mg/m³
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- 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:
- 1 000 mg/kg bw/day
- Value:
- 435 mg/m³
- Explanation for the modification of the dose descriptor starting point:
No inhalatory study available - Oral read across study used for route to route extrapolation
- AF for dose response relationship:
- 1
- Justification:
- Corrected NOEC
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic default
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Route-route concentration - No allometric scaling required
- AF for other interspecies differences:
- 2.5
- Justification:
- Default for interspecies variability - remaining differences in case of no other specific susceptibility differences info available.
- AF for intraspecies differences:
- 10
- Justification:
- General population default
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on target substance
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
- Explanation for the modification of the dose descriptor starting point:
The material is not classified for acute systemic effects, therefore derivation of acute DNEL is not required. Long-term DNELs are considered sufficient to ensure acute effects do not occur.
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:
- 5 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 200
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
No dermal study available - Oral read across study used for route to route extrapolation
- AF for dose response relationship:
- 1
- Justification:
- Corrected NOEC
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default for study animal rats.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default for interspecies variability - remaining differences in case of no other specific susceptibility differences info available.
- AF for intraspecies differences:
- 10
- Justification:
- Default value for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on target susbtance
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:
- 5 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 200
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
No route to route extrapolation necessary as is oral study.
- AF for dose response relationship:
- 1
- Justification:
- Default for NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value for study animal rats.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default for interspecies variability - remaining differences in case of no other specific susceptibility differences info available.
- AF for intraspecies differences:
- 10
- Justification:
- General population default
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on target substance
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
Long-term systemic inhalatory NOEC calculated based on the oral repeat dose NOAEL value as described in guidance R.8. The above factors were used to calculate a DNEL of 8.7 mg/m3.
Long-term systemic dermal NOEL calculated based on the oral repeat dose NOAEL value as described in guidance R.8. The above factors were used to calculate a DNEL of 5 mg/kg bw/day.
Long-term systemic oral NOEL provided by a developmental toxicity / teratogenicity study on the test substance was used to calculate the DNEL using the above assessment factors. The DNEL was 5 mg/kg bw/day.
No local effects were observed and therefore no DNEL derived.
The material is not classified for acute systemic effects, therefore derivation of acute DNELs is not required. Long-term DNELs are considered sufficient to ensure effects do not occur.
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.
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