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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: - | CAS number: -
- 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:
- 228.1 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
- Dose descriptor starting point:
- NOAEC
- Value:
- 11 350 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 5 703 mg/m³
- Explanation for the modification of the dose descriptor starting point:
A NOAEC of 11350 mg/m³, resulting from a 90d inhalation exposure repeated dose toxicity study was considered for the derivation of the DNEL. This NOAEC was corrected for DNEL derivation by considering difference in daily exposure (6 h/d in study, 8 h/d for workers) and considering differences in respiratory volume between rats as used in study and workers performing lightweight activities in line with ECHA guidance for derivation of DNELs.
NOAEC of 11350 mg/m³ * (6 h/d / 8 h/d) *(6.7 m³ (8h)/10 m³ (8h)) = 5’703 mg/m³ (corrected NOAEC)
- AF for dose response relationship:
- 1
- Justification:
- dose descriptor is a NOAEC from reliable study
- AF for differences in duration of exposure:
- 2
- Justification:
- sub-chronic to chronic assessment factor
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- rat - systemic effect (inhalation route) - not applicable for setting inhalation DNEL
- AF for other interspecies differences:
- 2.5
- Justification:
- systemic effect remaining differences according to guidance
- AF for intraspecies differences:
- 5
- Justification:
- workers default according to guidance
- AF for the quality of the whole database:
- 1
- Justification:
- good quality, subchronic data, supported by read-across reproductive data
- AF for remaining uncertainties:
- 1
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:
- 31.35 mg/kg bw/day
- 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):
- 100
- Dose descriptor starting point:
- NOAEC
- Value:
- 11 350 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 3 235 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
A NOAEC of 11350 mg/m³, resulting from a 90d inhalation exposure repeated dose toxicity study was considered for the derivation of the DNELdermal for workers. This NOAEC was corrected for DNEL derivation by considering difference in daily exposure (6 h/d in study, 8 h/d for workers) and considering conversion from NOAEC to NOAEL by multiplying with 0.38 m³/kg bw in line with ECHA guidance for derivation of DNELs.
NOAEC of 11350 mg/m³ * (6 h/d / 8 h/d) *(0.38 m³/kg bw) = 3’235 mg/m³ (corrected NOAEL dermal)
- AF for dose response relationship:
- 1
- Justification:
- dose descriptor is a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- sub-chronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- rat - systemic effect (dermal route)
- AF for other interspecies differences:
- 2.5
- Justification:
- systemic effect
- AF for intraspecies differences:
- 5
- Justification:
- workers
- AF for the quality of the whole database:
- 1
- Justification:
- good quality
- AF for remaining uncertainties:
- 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:
- low hazard (no threshold derived)
Additional information - workers
As “2-propanol and 2-butanol production, distn. residues” is not classified for acute toxicity, acute DNEL values do not have to be derived according to the REACH "Guidance on information requirements and chemical safety assessment Chapter R.8: Characterisation of dose [concentration]-response for human health". As the substance also did not show local effects (inhalation), no DNEL value had to be derived for local effects either.
As no information on dose-response for eye irritation and skin irritation is available, no DNEL was derived for these endpoints; the substance is classified for skin irritation (category 2) conservatively and for eye irritation (category 2) based on weak response in studies and thus considered of low hazard, without deriving a threshold. However, a qualitative approach to assessing and controlling the risks was followed.
For long-term effects, the toxicity to reproduction studies assessed for read-across substance are in line with the results seen in a sub-chronic inhalation toxicity study on the substance itself, supporting the NOAEC seen in this study of 11’350 mg/m³ to be chosen as basis for DNEL derivation for long term systemic toxicity. Corresponding DNELs were derived following the methodology as described in Guidance on information requirements and chemical safety assessment Chapter R.8: Characterisation of dose [concentration]-response for human health, November 2012.
In lack of detailed information on absorption rates and assuming similar absorption rates by inhalation, dermal and oral exposure, no correction for absorption via routes of exposure was applied.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 56.75 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
- Dose descriptor starting point:
- NOAEC
- Value:
- 11 350 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 2 838 mg/m³
- Explanation for the modification of the dose descriptor starting point:
A NOAEC of 11350 mg/m³, resulting from a 90d inhalation exposure repeated dose toxicity study was considered for the derivation of the DNEL. This NOAEC was corrected for DNEL derivation by considering difference in daily exposure (6 h/d in study, 24 h/d for general population) in line with ECHA guidance for derivation of DNELs.
NOAEC of 11350 mg/m³ * (6 h/d / 24 h/d) = 2’838 mg/m³ (corrected NOAEC)
- AF for dose response relationship:
- 1
- Justification:
- dose descriptor is a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- sub-chronic to chronic
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- rat - systemic effect (inhalation route)
- AF for other interspecies differences:
- 2.5
- Justification:
- systemic effect
- AF for intraspecies differences:
- 10
- Justification:
- general population
- AF for the quality of the whole database:
- 1
- Justification:
- good quality
- AF for remaining uncertainties:
- 1
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:
- 16.32 mg/kg bw/day
- 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):
- 200
- Dose descriptor starting point:
- NOAEC
- Value:
- 11 350 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 3 263 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
A NOAEC of 11350 mg/m³, resulting from a 90d inhalation exposure repeated dose toxicity study was considered for the derivation of the DNELdermal for workers. This NOAEC was corrected for DNEL derivation by considering difference in daily exposure (6 h/d in study, 24 h/d for general population) and considering conversion from NOAEC to NOAEL by multiplying with 1.15 m³/kg bw in line with ECHA guidance for derivation of DNELs.
NOAEC of 11350 mg/m³ * (6 h/d / 24 h/d) * (1.15 m³/kg bw) = 3’263 mg/m³ (corrected NOAEL dermal)
- AF for dose response relationship:
- 1
- Justification:
- dose descriptor is a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- sub-chronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- rat - systemic effect (dermal route)
- AF for other interspecies differences:
- 2.5
- Justification:
- systemic effect
- AF for intraspecies differences:
- 10
- Justification:
- general population
- AF for the quality of the whole database:
- 1
- Justification:
- good quality
- AF for remaining uncertainties:
- 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)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 16.32 mg/kg bw/day
- 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):
- 200
- Dose descriptor starting point:
- NOAEC
- Value:
- 13 053 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 3 263 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
A NOAEC of 11350 mg/m³, resulting from a 90d inhalation exposure repeated dose toxicity study was considered for the derivation of the DNELdermal for workers. This NOAEC was corrected for DNEL derivation by considering difference in daily exposure (6 h/d in study, 24 h/d for general population) and considering conversion from NOAEC to NOAEL by multiplying with 1.15 m³/kg bw in line with ECHA guidance for derivation of DNELs.
NOAEC of 11350 mg/m³ * (1.15 m³/kg bw) = 13053 mg/kg bw/d converted NOAEL (from NOAEC)
13053 mg/kg bw * (6 h/d / 24 h/d) = 3’263 mg/m³ (corrected NOAEL oral)
- AF for dose response relationship:
- 1
- Justification:
- dose descriptor is a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- sub-chronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- rat - systemic effect (oral route)
- AF for other interspecies differences:
- 2.5
- Justification:
- systemic effect
- AF for intraspecies differences:
- 10
- Justification:
- general population
- AF for the quality of the whole database:
- 1
- Justification:
- good quality
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - General Population
As “2-propanol and 2-butanol production, distn. residues” is not classified for acute toxicity, acute DNEL values do not have to be derived according to the REACH "Guidance on information requirements and chemical safety assessment Chapter R.8: Characterisation of dose [concentration]-response for human health". As the substance also did not show local effects (inhalation), no DNEL value had to be derived for local effects either.
As no information on dose-response for eye irritation and skin irritation is available, no DNEL was derived for these endpoints; the substance is classified for skin irritation (category 2) conservatively and for eye irritation (category 2) based on weak response in studies and thus considered of low hazard, without deriving a threshold. However, a qualitative approach to assessing and controlling the risks was followed.
For long-term effects, the toxicity to reproduction studies assessed for read-across substance are in line with the results seen in a sub-chronic inhalation toxicity study on the substance itself, supporting the NOAEC seen in this study of 11’350 mg/m³ to be chosen as basis for DNEL derivation for long term systemic toxicity. Corresponding DNELs were derived following the methodology as described in Guidance on information requirements and chemical safety assessment Chapter R.8: Characterisation of dose [concentration]-response for human health, November 2012.
In lack of detailed information on absorption rates and assuming similar absorption rates by inhalation, dermal and oral exposure, no correction for absorption via routes of exposure was applied.
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.