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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 204-817-5 | CAS number: 126-98-7
- 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:
- 1.26 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 31.54 mg/m³
- AF for dose response relationship:
- 1
- Justification:
- An assessment factor of 1 is applicable when the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 2
- Justification:
- Default ECHA AF for subchronic to chronic studies, applicable to results from sub-chronic (90 day) study.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Allometric scaling omitted since differences in breathing (rat to human) accounted for in modification of starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default AF for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- ECHA default AF for worker population
- AF for the quality of the whole database:
- 1
- Justification:
- Key study is considered reliable and the database is comprehensive.
- AF for remaining uncertainties:
- 1
- Justification:
- None considered relevant.
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
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:
- 0.075 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
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 7.5 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Route to route extrapolation required for oral to dermal route as no long term dermal study available.
- AF for dose response relationship:
- 1
- Justification:
- An assessment factor of 1 is applicable when the starting point is a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Default ECHA AF for subchronic to chronic studies, applicable to results from sub-chronic (90 day) study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- ECHA default AF for allometric scaling for rats to humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default AF for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- ECHA default AF for worker population
- AF for the quality of the whole database:
- 1
- Justification:
- Key study is considered reliable and the database is comprehensive.
- AF for remaining uncertainties:
- 1
- Justification:
- None considered relevant.
Acute/short term exposure
- Hazard assessment conclusion:
- no DNEL required: short term exposure controlled by conditions for long-term
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- no DNEL required: short term exposure controlled by conditions for long-term
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
The worker DNELs derived for long-term systemic effects (inhalation and dermal) have been derived using standard assessment factors as recommended by ECHA (Guidance on information requirements and chemical safety assessment; Chapter R.8: Characterisation of dose [concentration]-response for human health).
The substance is classified for acute toxicity for inhalation and dermal routes, but acute systemic DNELs are not derived as available acute studies do not provide sufficient dose-response relationship data. In addition the long-term DNELs are protective of short-term exposure because the industrial environment is strictly moderated, high peak exposures are not expected, and risk management measures will prevent inhalation and dermal exposure.
The substance may have some potential to cause irritation, but local DNELs are not derived as systemic toxicity is the primary human health concern and the industrial measures in place to prevent exposure will also cover local effects.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.31 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 15.69 mg/m³
- AF for dose response relationship:
- 1
- Justification:
- An assessment factor of 1 is applicable when the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 2
- Justification:
- Default ECHA AF for subchronic to chronic studies, applicable to results from sub-chronic (90 day) study.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Allometric scaling omitted since differences in breathing (rat to human) accounted for in modification of starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default AF for remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- ECHA default AF for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Key study is considered reliable and the database is comprehensive.
- AF for remaining uncertainties:
- 1
- Justification:
- None considered relevant.
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
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:
- 0.037 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
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 7.5 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Route to route extrapolation required for oral to dermal route as no long term dermal study available.
- AF for dose response relationship:
- 1
- Justification:
- An assessment factor of 1 is applicable when the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 2
- Justification:
- Default ECHA AF for subchronic to chronic studies, applicable to results from sub-chronic (90 day) study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- ECHA default AF for allometric scaling for rats to humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default AF for remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- ECHA default AF for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Key study is considered reliable and the database is comprehensive.
- AF for remaining uncertainties:
- 1
- Justification:
- None considered relevant.
Acute/short term exposure
- Hazard assessment conclusion:
- no DNEL required: short term exposure controlled by conditions for long-term
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.037 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
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 7.5 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- An assessment factor of 1 is applicable when the starting point is a NOAEL.
- AF for differences in duration of exposure:
- 2
- Justification:
- Default ECHA AF for subchronic to chronic studies, applicable to results from sub-chronic (90 day) study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- ECHA default AF for allometric scaling for rats to humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default AF for remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- ECHA default AF for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Key study is considered reliable and the database is comprehensive.
- AF for remaining uncertainties:
- 1
- Justification:
- None considered relevant.
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
All uses of the substance are industrial. There are no general public/consumer uses so no exposure is expected.
No exposure of the general population is expected under normal industrial operating conditions. Nevertheless, long-term systemic DNELs have been calculated in case it becomes necessary to assess long-term exposure from articles and any indirect exposure from the environment.
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.