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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 701-092-1 | CAS number: 1175006-92-4
- 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:
- 3.52 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):
- 75
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 264 mg/m³
- Explanation for the modification of the dose descriptor starting point:
8 h exposure time, extrapolation from 50% bioavailability oral to 100% bioavailability inhalation, no inhalation study available
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not for concentrations
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- default factor for worker
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 17.5 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 75
- Dose descriptor:
- other: NO(A)EL = 500 mg/kg bw/day (repeated dose dermal study), 8 h exposure = 0.38 m^3/kg bw (respiratory volume for rat), NOAEC = 1315 mg/m^3/day
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic (required for inhalation as for systemic effects)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not for concentrations
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- default factor for worker
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 3.3 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 300
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
not required: NO(A)EL from repeated dose dermal study
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- allometric scaling factor rat-human
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- default factor for worker
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.8 mg/cm²
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 5
- Dose descriptor:
- other: NOAEL
- AF for dose response relationship:
- 1
- Justification:
- LOAEL is 1000 mg/kg bw/day (LOAEC = 8 mg/cm^2) and NOEL is 500 mg/kg bw/day (NOAEC = 4 mg/cm^2); as rational, NOAEL could be = NOEL
- AF for differences in duration of exposure:
- 1
- Justification:
- the toxic effect is driven by the exposure concentraiton
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- no allometric scaling for local effects
- AF for other interspecies differences:
- 1
- Justification:
- effects on skin via simple destruction of membranes
- AF for intraspecies differences:
- 5
- Justification:
- default factor for worker
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- high hazard (no threshold derived)
Additional information - workers
The long-term inhalation DNEL for systemic effects is derived on the basis of the sub-acute oral toxicity study. The calculated DNEL is 3.5 mg/m^3, applying the assessment factor of 75.
The long-term inhalation DNEL for local effects is derived on the basis of the sub-acute dermal toxicity study (2-week study), since 1000 mg/kg bw/day dose was considered as LOAEL for local effects. For this DNEL derivation NOEL = 500 mg/kg bw/day was used. The calculated DNEL is 17.5 mg/m^3, applying the assessment factor of 75.
The acute/short term exposure inhalation DNEL for systemic and local effects was not assessed, since no acute inhalation study is available and Mexoryl SBO shows low acute toxicity when administered orally (LD50 > 2000 mg/kg bw).
The long-term dermal DNEL for systemic effects is derived on the basis of sub-acute dermal toxicity study (2-week study), where NOEL was 1000 mg/kg bw/day, the highest administered dose of Mexoryl SBO. The calculated DNEL is 3.3 mg/kg bw/day, applying the assessment factor of 300.
The long-term dermal DNEL for local effects is derived on the basis of the sub-acute dermal toxicity study (2-week study), where starting point is NOEL = 500 mg/kg bw/day (NOAEC = 4 mg/cm^2). The calculated DNEL is 0.8 mg/cm^2, applying the assessment factor of 5.
The acute/short term exposure dermal DNEL for systemic and local effects was not assessed, since no acute dermal study is available and Mexoryl SBO shows low acute toxicity when administered orally (LD50 > 2000 mg/kg bw).
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.87 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):
- 150
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 130 mg/m³
- Explanation for the modification of the dose descriptor starting point:
24 h exposure time, extrapolation from 50% bioavailability oral to 100% bioavailability inhalation, no inhalation study available
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not required for concentration
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- general population
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 8.8 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 150
- Dose descriptor:
- other: NO(A)EL = 500 mg/kg bw/day (repeated dose dermal study), 8 h exposure = 0.38 m^3/kg bw (respiratory volume for rat), NOAEC = 1315 mg/m^3/day
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic (required for inhalation as for systemic effects)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not for concentrations
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- default factor for general population
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- no required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.7 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
not required: NO(A)EL from repeated dose dermal study
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- allometric scaling factor rat-human
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- default factor for general population
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.4 mg/cm²
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 10
- Dose descriptor:
- other: LOAEL
- AF for dose response relationship:
- 1
- Justification:
- LOAEL is 1000 mg/kg bw/day (LOAEC = 8 mg/cm^2) and NOEL is 500 mg/kg bw/day (NOAEC = 4 mg/cm^2); as rational, NOAEL = NOEL
- AF for differences in duration of exposure:
- 1
- Justification:
- the toxic effect is driven by the exposure concentraiton
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- no allometric scaling for local effects
- AF for other interspecies differences:
- 1
- Justification:
- effects on skin via simple destruction of membranes
- AF for intraspecies differences:
- 10
- Justification:
- default factor for general population
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
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:
- 0.5 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):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 300 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
no route-to-route extrapolation performed
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from sub-acute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- extrapolation rat to human
- AF for other interspecies differences:
- 2.5
- Justification:
- remaining differences
- AF for intraspecies differences:
- 10
- Justification:
- general population
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
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:
- high hazard (no threshold derived)
Additional information - General Population
The long-term inhalation DNEL for systemic effects is derived on the basis of the sub-acute oral toxicity study. The calculated DNEL is 0.87 mg/m^3, applying the assessment factor of 150.
The long-term inhalation DNEL for local effects is derived on the basis of the sub-acute dermal toxicity study (2-week study), since 1000 mg/kg bw/day dose was considered as LOAEL for local effects. For this DNEL derivation NOEL = 500 mg/kg bw/day was used. The calculated DNEL is 8.8 mg/m^3, applying the assessment factor of 150.
The acute/short term exposure inhalation DNEL for systemic and local effects was not assessed, since no acute inhalation study is available and Mexoryl SBO shows low acute toxicity when administered orally (LD50 > 2000 mg/kg bw).
The long-term dermal DNEL for systemic effects is derived on the basis of sub-acute dermal toxicity study (2-week study), where NOEL was 1000 mg/kg bw/day, the highest administered dose of Mexoryl SBO. The calculated DNEL is 1.7 mg/kg bw/day, applying the assessment factor of 600.
The long-term dermal DNEL for local effects is derived on the basis of the sub-acute dermal toxicity study (2-week study), where starting point is NOEL = 500 mg/kg bw/day (NOAEC = 4 mg/cm^2). The calculated DNEL is 0.4 mg/cm^2, applying the assessment factor of 10.
The acute/short term exposure dermal DNEL for systemic and local effects was not assessed, since no acute dermal study is available and Mexoryl SBO shows low acute toxicity when administered orally (LD50 > 2000 mg/kg bw).
The long-term oral DNEL for systemic effects is derived on the basis of sub-acute oral toxicity study. The calculated DNEL is 0.5 mg/kg bw/day, applying the assessment factor of 600.
The acute/short term exposure oral DNEL for systemic effects was not assessed, since Mexoryl SBO shows low acute toxicity when administered orally (LD50 > 2000 mg/kg bw).
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.