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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 269-144-1 | CAS number: 68188-18-1
- 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:
- 3.81 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):
- 12.5
- Dose descriptor starting point:
- LOAEL
- Value:
- 70 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 47.63 mg/m³
- Explanation for the modification of the dose descriptor starting point:
LOAEL fetal: 70 mg/kg bw/day (Low Observed Adverse Effect Level)
-> NOAEL = 70/3 = 23.3Corrected inhalatory NOAEL = (23,3/2.4 (rabbit) x 70/10 x7/5 x50/100 )
NOAEC = 47.63 mg/m³
Expose in animal study/exposure in humans = 7/5 (default worker)
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- 1 (complete organogenese)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Already covered by correction of starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default value
- AF for intraspecies differences:
- 5
- Justification:
- ECHA default value
- AF for the quality of the whole database:
- 1
- Justification:
- The default assessment factor to be applied for good/standard quality of the database, taking into account completeness, consistency and the standard information requirements, is 1.
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
- DNEL derivation method:
- other: ECHA guidance
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
- DNEL derivation method:
- other: ECHA guidance
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.09 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):
- 30
- Dose descriptor starting point:
- LOAEL
- Value:
- 70 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 32.6 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
LOAEL fetal: 70 mg/kg bw/day (Low Observed Adverse Effect Level)
-> NOAEL = 70/3 = 23.3Corrected human NOAEL = 32.6 mg/kg (23.3 x 7/5)
Expose in animal study/exposure in humans = 7/5 (default worker)- AF for dose response relationship:
- 1
- Justification:
- When the starting point is a NOAEL, the default assessment factor, as a standard procedure, is 1.
- AF for differences in duration of exposure:
- 1
- Justification:
- 1 (complete organogenese)
- AF for interspecies differences (allometric scaling):
- 2.4
- Justification:
- Default allometric scaling factor for rabbit to human. 2.4 (default)
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA suggests a default factor of 2.5 for remaining interspecies differences.
- AF for intraspecies differences:
- 5
- Justification:
- ECHA default value
- AF for the quality of the whole database:
- 1
- Justification:
- The default assessment factor to be applied for good/standard quality of the database, taking into account completeness, consistency and the standard information requirements, is 1.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
Acute toxicity:
Systemic toxicity:
Acute oral: LD50 1271 mg/kg; non-specific signs of toxicity were observed, including depression, ruffles fur and dyspnoea. The signs tended to persist longer in the higher dosages where animals survived the investigation period. No particular specific effect was noted in the body weight data. Gross necropsy observations were also non-specific in animals at termination. Rats which died during the first few days after dosing showed gastrointestinal lesions and some other congested organs. The cause of death of these animals may have been related to the intestinal lesions. Histopathology was not performed.
Local effects:
Acute dermal: Solely irritant potency on skin detected. The same applies for skin and eye irritation studies. The substance is classified with Skin Irrit Cat. 2 (Regulation (EU) 1272/2008); according to ECHA Guidance ECHA Guidance Part E: Risk Characterisation (May 2016) this translates into “low hazard”.
Developmental toxicity/teratogenicity:
Systemic toxicity:
LOAEL fetal: 70 mg/kg bw/day (Low Observed Adverse Effect Level)
-> NOAEL = 70/3 = 23.3
Corrected human NOAEC = 47.63 mg/m³ (23,3/2.4 (rabbit) x 70 / 10 x7/5 x50/100)
DNEL (systemic long term) = 3.81 mg/m³ (47.63 / 12.5)
Expose in animal study/exposure in humans = 7/5 (default worker)
Local toxicity:
The substance is classified with Skin Irrit Cat. 2 (Regulation (EU) 1272/2008); according to ECHA Guidance ECHA Guidance Part E: Risk Characterisation (May 2016) this translates into “low hazard”.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.68 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:
- LOAEL
- Value:
- 70 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 17.01 mg/m³
- Explanation for the modification of the dose descriptor starting point:
LOAEL fetal: 70 mg/kg bw/day (Low Observed Adverse Effect Level)
-> NOAEL = 70/3 = 23.3Corrected inhalatory NOAEL = (23.3 / 2.4 x 70 / 20 x 50/100)
NOAEC = 17.01 mg/m³- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- 1 (complete organogenese)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Already covered by correction of starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- default value
- AF for intraspecies differences:
- 10
- Justification:
- ECHA guidance
- AF for the quality of the whole database:
- 1
- Justification:
- The default assessment factor to be applied for good/standard quality of the database, taking into account completeness, consistency and the standard information requirements, is 1.
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.39 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):
- 60
- Dose descriptor starting point:
- LOAEL
- Value:
- 70 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 23.3 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
LOAEL fetal: 70 mg/kg bw/day (Low Observed Adverse Effect Level)
-> NOAEL = 70/3 = 23.3- AF for dose response relationship:
- 1
- Justification:
- When the starting point is a NOAEL, the default assessment factor, as a standard procedure, is 1.
- AF for differences in duration of exposure:
- 1
- Justification:
- 1 (complete organogenese)
- AF for interspecies differences (allometric scaling):
- 2.4
- Justification:
- Default allometric scaling factor for rabbit to human.
2.4 (default) - AF for other interspecies differences:
- 2.5
- Justification:
- Echa default value
- AF for intraspecies differences:
- 10
- Justification:
- ECHA default value
- AF for the quality of the whole database:
- 1
- Justification:
- The default assessment factor to be applied for good/standard quality of the database, taking into account completeness, consistency and the standard information requirements, is 1.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.39 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):
- 60
- Dose descriptor starting point:
- LOAEL
- Value:
- 70 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 23.3 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
LOAEL fetal: 70 mg/kg bw/day (Low Observed Adverse Effect Level)
-> NOAEL = 70/3 = 23.3- AF for dose response relationship:
- 1
- Justification:
- When the starting point is a NOAEL, the default assessment factor, as a standard procedure, is 1.
- AF for differences in duration of exposure:
- 1
- Justification:
- 1 (complete organogenese)
- AF for interspecies differences (allometric scaling):
- 2.4
- Justification:
- Default allometric scaling factor for rabbit to human.
2.4 (default) - AF for other interspecies differences:
- 2.5
- Justification:
- default value
- AF for intraspecies differences:
- 10
- Justification:
- ECHA default value
- AF for the quality of the whole database:
- 1
- Justification:
- The default assessment factor to be applied for good/standard quality of the database, taking into account completeness, consistency and the standard information requirements, is 1.
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:
- low hazard (no threshold derived)
Additional information - General Population
Local effects:
Acute dermal: Solely irritant potency on skin detected. The same applies for skin and eye irritation studies. The substance is classified with Skin Irrit Cat. 2 (Regulation (EU) 1272/2008); according to ECHA Guidance ECHA Guidance Part E: Risk Characterisation (May 2016) this translates into “low hazard”.
Systemic effects:
See for further details "Additional information for worker"
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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