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Diss Factsheets
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EC number: 701-368-1 | CAS number: 1962138-75-5
- 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:
- 6.71 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:
- 85 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 168 mg/m³
- Explanation for the modification of the dose descriptor starting point:
Default (DNEL calculator)
- AF for dose response relationship:
- 1
- Justification:
- Default (DNEL calculator)
- AF for differences in duration of exposure:
- 2
- Justification:
- Default (DNEL calculator)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Default (DNEL calculator)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default (DNEL calculator)
- AF for intraspecies differences:
- 5
- Justification:
- Default (DNEL calculator)
- AF for the quality of the whole database:
- 1
- Justification:
- Default (DNEL calculator)
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:
- 119 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:
- 85 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 11 900 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The substance fulfils the information requirements in accordance with ECHA guidance R7.5 -7.7 (2016) for assessing long-term systemic toxicity. Since no repeated dose dermal study is available, route-to-route extrapolation from the oral exposure route is performed. The starting point is the NOAEL from the 9 -months oral study in rats; 85 mg/kg bw/day.
Based on data from a dermal absorption study of a C12LAS homologue in isolated human epidermis (Howes, 1975), < 0.065% of the applied dose penetrated the skin in 48 hours. An oral absorption value of 80 -90% was experimentally derived. A route-to-route factor of 100, instead of 80/0.065=1230.8, was conservatively assumed. A correction for 5 day exposure is performed (7 days exposure per week in the study versus 5 days per week for workers); therefore the modified starting point = 85 x 100 x (7/5) = 11,900 mg/kg bw/day.
- AF for dose response relationship:
- 1
- Justification:
- The starting point for the DNEL calculation is a NOAEL, derived from a study which is of good quality and without uncertainties. Therefore the default assessment factor is 1.
- AF for differences in duration of exposure:
- 2
- Justification:
- The starting point for DNEL derivation is a sub-chronic study, hence the extrapolation to chronic exposure results in a factor of 2.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Since the starting point is an oral study and extrapolation to dermal route of exposure will need allometric scaling. For rats, the default assessment factor, as a standard procedure, is 4.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default
- AF for intraspecies differences:
- 5
- Justification:
- Default for workers
- AF for the quality of the whole database:
- 1
- Justification:
- Default for good quality database is 1.
- AF for remaining uncertainties:
- 1
- Justification:
- Since there are no further uncertainties, the default assessment factor is 1.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
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)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - workers
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.18 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:
- 85 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 59.2 mg/m³
- Explanation for the modification of the dose descriptor starting point:
Default (DNEL calculator)
- AF for dose response relationship:
- 1
- Justification:
- Default (DNEL calculator)
- AF for differences in duration of exposure:
- 2
- Justification:
- Default (DNEL calculator)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Default (DNEL calculator)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default (DNEL calculator)
- AF for intraspecies differences:
- 10
- Justification:
- Default (DNEL calculator)
- AF for the quality of the whole database:
- 1
- Justification:
- Default (DNEL calculator)
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:
- 42.5 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:
- 85 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 8 500 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The substance fulfils the information requirements in accordance with ECHA guidance R7.5 -7.7 (2016) for assessing long-term systemic toxicity. Since no repeated dose dermal study is available, route-to-route extrapolation from the oral exposure route is performed. The starting point is the NOAEL from the 9 -months oral study in rats; 85 mg/kg bw/day.
Based on data from a dermal absorption study of a C12LAS homologue in isolated human epidermis (Howes, 1975), < 0.065% of the applied dose penetrated the skin in 48 hours. An oral absorption value of 80 -90% was experimentally derived. A route-to-route factor of 100, instead of 80/0.065=1230.8, was conservatively assumed. Therefore the modified starting point = 85 x 100 = 8500 mg/kg bw/day.
- AF for dose response relationship:
- 1
- Justification:
- The starting point for the DNEL calculation is a NOAEL, derived from a study which is of good quality and without uncertainties. Therefore the default assessment factor, as a standard procedure, is 1.
- AF for differences in duration of exposure:
- 2
- Justification:
- The starting point for the DNEL calculation is a NOAEL from sub-chronic study. Therefore extrapolation to chronic exposure will result in the application of an assessment factor of 2.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Since the starting point for DNEL derivation is from an oral study and the extrapolation into the dermal exposure route will result into application of allometric scaling factor. For rats, the default assessment factor, as a standard procedure, is 4.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default
- AF for intraspecies differences:
- 10
- Justification:
- Default for general population
- AF for the quality of the whole database:
- 1
- Justification:
- The database is of good quality.
- AF for remaining uncertainties:
- 1
- Justification:
- No remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
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:
- 0.425 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:
- 85 mg/kg bw/day
- Value:
- 85 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Default (DNEL calculator)
- AF for dose response relationship:
- 1
- Justification:
- Default (DNEL calculator)
- AF for differences in duration of exposure:
- 2
- Justification:
- Default (DNEL calculator)
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default (DNEL calculator)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default (DNEL calculator)
- AF for intraspecies differences:
- 10
- Justification:
- Default (DNEL calculator)
- AF for the quality of the whole database:
- 1
- Justification:
- Default (DNEL calculator)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - General Population
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