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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 228-408-6 | CAS number: 6259-76-3
- 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:
- 1.7 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):
- 75
- Dose descriptor starting point:
- NOAEC
- Value:
- 249 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 125 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The NOAEC of 249 mg/m3 from the 28-day inhalation study is corrected for the duration of exposure (*6/8) and respiratory volume (*6.7/10), to give a corrected NOAEC of 125 mg/m3.
- AF for dose response relationship:
- 1
- Justification:
- Default value
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from a sub-acute study to long-term exposure.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Allometric factors are already accounted for in derivation of the corrected starting point.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 5
- Justification:
- Default value for workers
- AF for the quality of the whole database:
- 1
- Justification:
- Good quality database
- 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:
- 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:
- 6.4 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:
- 50 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 641 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The NOAEL of 50 mg/kg bw/d from the 90-day rat study with isoamyl salicylate is corrected for the extent of oral absorption (100%) and dermal absorption of 7.8%.
- AF for dose response relationship:
- 1
- Justification:
- Default value
- AF for differences in duration of exposure:
- 2
- Justification:
- Extrapolation from a sub-chronic study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value: starting point is a rat study.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 5
- Justification:
- Deafult value (workers)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value: good quality database
- AF for remaining uncertainties:
- 1
- Justification:
- Default value: no significant remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 885 µg/cm²
- Most sensitive endpoint:
- sensitisation (skin)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 40
- Dose descriptor:
- other: The starting point is the Weight of Evidence No Expected Sensitisation Induction Level (NESIL) for hexyl salicylate of 35400 μg/cm2 from human data.
- Value:
- 354 000 mg/m³
- AF for dose response relationship:
- 1
- Justification:
- Not applicable
- AF for differences in duration of exposure:
- 1
- Justification:
- Not applicable
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not applicable
- AF for other interspecies differences:
- 1
- Justification:
- Not required - starting point is a human study
- AF for intraspecies differences:
- 5
- Justification:
- Default value (workers)
- AF for the quality of the whole database:
- 2
- Justification:
- Default value
- AF for remaining uncertainties:
- 2
- Justification:
- An additional assessment factor of 2 is applied to take into account potential matrix effects.
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 885 µg/cm²
- Most sensitive endpoint:
- sensitisation (skin)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 40
- Dose descriptor starting point:
- other: The starting point is the Weight of Evidence No Expected Sensitisation Induction Level (NESIL) for hexyl salicylate of 35400 μg/cm2 from human data.
- Value:
- 354 000 mg/m³
- AF for dose response relationship:
- 1
- Justification:
- Not applicable
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not applicable
- AF for other interspecies differences:
- 1
- Justification:
- Not applicable
- AF for intraspecies differences:
- 5
- Justification:
- Default value (workers)
- AF for the quality of the whole database:
- 2
- Justification:
- Default value
- AF for remaining uncertainties:
- 2
- Justification:
- An additional assessment factor of 2 is applied to take into account potential matrix effects.
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
DNEL derivation: workers
Systemic inhalation DNEL values
The NOAEC of 249 mg/m3 from the 28-day inhalation study is corrected for the duration of exposure (*6/8) and respiratory volume (*6.7/10), to give a corrected NOAEC of 125 mg/m3. Individual assessment factors of 1 (for dose-response relationship), 6 (for duration of exposure), 2.5 (for other interspecies differences), 5 (for intraspecies differences), 1 (for database quality) and 1 (for remaining uncertainties) give an overall assessment factor of 75. Applying the AF to the corrected starting point gives a long-term DNEL of 1.7 mg/m3.
In the absence of any identified hazard, a short-term systemic inhalation DNEL is not derived.
Local inhalation DNEL values
No hazard is identified. No local effects were observed at any exposure level in a 28 -day inhalation study with hexyl salicylate. Local inhalation DNELs are therefore not derived.
Systemic dermal DNEL values
The NOAEL of 50 mg/kg bw/d from the 90-day rat study with isoamyl salicylate is corrected for the extent of oral absorption (100%) and dermal absorption of 7.8% to give a corrected starting point of 641 mg/kg bw/d. Individual assessment factors of 1 (for dose-response relationship), 2 (for duration of exposure), 4 (for allometric differences), 2.5 (for other interspecies differences), 5 (for intraspecies differences), 1 (for database quality) and 1 (for remaining uncertainties) give an overall assessment factor of 100. Applying the AF to the corrected starting point gives a DNEL of 6.4 mg/kg bw/d.
In the absence of any identified hazard, a short-term systemic demal DNEL is not derived.
Local dermal DNEL values
Hexyl salicylate is classified for skin sensitisation in Category 1B. The starting point is the Weight of Evidence No Expected Sensitisation Induction Level (NESIL) for hexyl salicylate of 35400 µg/cm2 from human data. Individual assessment factors of 1 (for duration), 2 (for data quality), 2 (for matrix effects), 2 (for conditions of exposure), 5 (for intraspecies differences) and 1 (for interspecies differences) results in an overall assessment factor of 40. Application of the overall assessment factor results in long-term local dermal DNEL values (short-term and long-term) of 885 µg/cm2.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.4 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):
- 150
- Dose descriptor starting point:
- NOAEC
- Value:
- 249 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 62 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The NOAEC from the 28-day inhalation study is corrected for the duration of exposure (*6/24). Individual assessment factors of 1 (for dose-response relationship), 6 (for duration of exposure), 2.5 (for other interspecies differences), 10 (for intraspecies differences), 1 (for database quality) and 1 (for remaining uncertainties) give an overall assessment factor of 150. Applying the AF to the corrected starting point gives a DNEL of 0.4 mg/m3.
- AF for dose response relationship:
- 1
- Justification:
- The starting point was a NOAEC
- Justification:
- Extrapolation from sub-acute study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not required: already accounted for
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value (starting point is a rat study)
- AF for intraspecies differences:
- 10
- Justification:
- Default value (general population)
- AF for the quality of the whole database:
- 1
- Justification:
- Good quality database
- AF for remaining uncertainties:
- 1
- Justification:
- No remaining uncertainties.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
- AF for remaining uncertainties:
- 2
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:
- 3.2 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:
- 50 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 641 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The NOAEL of 50 mg/kg bw/d from the 90-day rat study with isoamyl salicylate is corrected for the extent of oral absorption (100%) and dermal absorption of 7.8% to give a corrected starting point of 641 mg/kg bw/d.
- AF for dose response relationship:
- 1
- Justification:
- The starting point used was an NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Extrapolation from sub-chronic to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value (starting point was a rat study)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 10
- Justification:
- Default value (general population)
- AF for the quality of the whole database:
- 1
- Justification:
- Good quality database
- 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:
- DNEL (Derived No Effect Level)
- Value:
- 442.5 µg/cm²
- Most sensitive endpoint:
- sensitisation (skin)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 80
- Dose descriptor:
- other: NESIL
- Value:
- 354 000 mg/m³
- AF for dose response relationship:
- 1
- Justification:
- Not required
- AF for differences in duration of exposure:
- 1
- Justification:
- Not relevant
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not relevant
- AF for other interspecies differences:
- 1
- Justification:
- Not relevant
- AF for intraspecies differences:
- 10
- Justification:
- Default value (general population)
- AF for the quality of the whole database:
- 2
- AF for remaining uncertainties:
- 2
- Justification:
- An additional assessment factor of 2 is applied to take into account potential matrix effects.
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 442.5 µg/cm²
- Most sensitive endpoint:
- sensitisation (skin)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 80
- Dose descriptor starting point:
- other: NESIL
- Value:
- 354 000 mg/m³
- AF for dose response relationship:
- 1
- Justification:
- Not required
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not required
- AF for other interspecies differences:
- 1
- Justification:
- Not required
- AF for intraspecies differences:
- 10
- Justification:
- Default value (geeral population)
- AF for the quality of the whole database:
- 2
- Justification:
- Default value
- AF for remaining uncertainties:
- 2
- Justification:
- An additional assessment factor of 2 is applied to take into account potential matrix effects.
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.3 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:
- 50 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Not required: the starting point is an oral study.
- AF for dose response relationship:
- 1
- Justification:
- Default value: the starting point is a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Extrapolation from sub-chronic study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value: starting point is the rat study
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 10
- Justification:
- Default value (general population
- AF for the quality of the whole database:
- 1
- Justification:
- Good quality database
- AF for remaining uncertainties:
- 1
- Justification:
- No remaining uncertainties
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
DNEL derivation: general population
Systemic inhalation DNEL values
The NOAEC of 249 mg/m3 from the 28-day inhalation study is corrected for the duration of exposure (*6/24), to give a corrected NOAEC of 62 mg/m3. Individual assessment factors of 1 (for dose-response relationship), 6 (for duration of exposure), 2.5 (for other interspecies differences), 10 (for intraspecies differences), 1 (for database quality) and 1 (for remaining uncertainties) give an overall assessment factor of 150. Applying the AF to the corrected starting point gives a long-term DNEL of 0.4 mg/m3.
In the absence of any identified hazard, a short-term systemic inhalation DNEL is not derived.
Local inhalation DNEL values
No hazard is identified. No local effects were observed at any exposure level in a 28 -day inhalation study with hexyl salicylate. Local inhalation DNELs are therefore not derived.
Systemic dermal DNEL values
The NOAEL of 50 mg/kg bw/d from the 90-day rat study with isoamyl salicylate is corrected for the extent of oral absorption (100%) and dermal absorption of 7.8% to give a corrected starting point of 641 mg/kg bw/d. Individual assessment factors of 1 (for dose-response relationship), 2 (for duration of exposure), 4 (for allometric differences), 2.5 (for other interspecies differences), 10 (for intraspecies differences), 1 (for database quality) and 1 (for remaining uncertainties) give an overall assessment factor of 200. Applying the AF to the corrected starting point gives a DNEL of 3.2 mg/kg bw/d.
In the absence of any identified hazard, a short-term systemic demal DNEL is not derived.
Local dermal DNEL values
Hexyl salicylate is classified for skin sensitisation in Category 1B. The starting point is the Weight of Evidence No Expected Sensitisation Induction Level (NESIL) for hexyl salicylate of 35400 µg/cm2 from human data. Individual assessment factors of 1 (for duration), 2 (for data quality), 2 (for matrix effects), 2 (for conditions of exposure), 10 (for intraspecies differences) and 1 (for interspecies differences) results in an overall assessment factor of 40. Application of the overall assessment factor results in local (short-term an long-term) dermal DNELs of 442.5 µg/cm2.
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