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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 701-164-2 | CAS number: -
- 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:
- 1.234 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:
- 25 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 30.855 mg/m³
- Explanation for the modification of the dose descriptor starting point:
Starting point: NOAEL (oral route, subchronic) = 25 mg/kg bw/day
Correction factor for differences in respiratory volume (rat/workers): 1/0.38
Correction factor for light activity at work: 6.7/10
Correction factor for difference between human and experimental exposure conditions: 7/5 (In the study, animals were exposed 7 days per week, and workers work 5 days per week).
Absorptions by inhalation and oral route are not known; therefore, it was considered that oral absorption in the rat was 50% less effective than the human absorption by inhalation in accordance with ECHA Guidance.
NOAEC = NOAEL x (1/0.38) x (6.7/10) x 0.5 x 7/5 = 25 x (1/0.38) x (6.7/10) x 0.5 x 7/5 = 30.85526316 mg/m3- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic exposure to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- ECHA REACH Guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 5
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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:
- 0.35 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:
- 25 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 35 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Starting point: NOAEL (oral route, subchronic) = 25 mg/kg bw/day
Correction factor for difference between human and experimental exposure conditions: 7/5 (In the study, animals were exposed 7 days per week, and workers work 5 days per week).
Absorptions by dermal and oral routes are not known; therefore, it was considered that oral absorption in the rat was equivalent to human absorption via the dermal route in accordance with ECHA Guidance.
NOAEL = NOAEL x 1 x 7/5 = 25 x 1 x 7/5 = 35 mg/kg bw/d- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic exposure to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 5
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
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:
- 0.217 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):
- 50
- Dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 10.87 mg/m³
- Explanation for the modification of the dose descriptor starting point:
Starting point: NOAEL (oral route, subchronic) = 25 mg/kg bw/day
Correction factor for differences in respiratory volume (rat/general population): 1/1.15
Absorptions by inhalation and oral route are not known, therefore it was considered that oral absorption in the rat was 50% less effective than the human absorption by inhalation in accordance with ECHA Guidance.
NOAEC = NOAEL x (1/1.15) x 0.5 = 25 x (1/1.15) x 0.5 = 10.86956522 mg/m3- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic exposure to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- ECHA REACH Guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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:
- 0.125 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):
- 200
- Dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Starting point: NOAEL (oral route, subchronic) = 25 mg/kg bw/day
Absorptions by dermal and oral routes are not known, therefore it was considered that oral absorption in the rat was equivalent to human absorption via the dermal route in accordance with ECHA Guidance.
NOAEL = NOAEL x 1 = 25 x 1 = 25 mg/kg bw/day- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic exposure to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.125 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):
- 200
- Dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
No modification of the dose descriptor starting point is required.
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic exposure to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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
The registered substance is classified as Skin Sens. 1; H317 based on available experimental data.
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.