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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.
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EC number: 500-097-4 | CAS number: 37353-75-6 1 - 4.5 moles propoxylated
- 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:
- 2.12 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
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 52.89 mg/m³
- Explanation for the modification of the dose descriptor starting point:
A NOAEL for the oral route needs to be converted for inhalation considering the differences between the routes and exposure between the test animals (rats) and workers and the general population.
Workers: As the NOAEL was obtained on rats using the oral route, it must be corrected for an inhalation exposure of workers, taking into account that workers are considered to be working 8h/d, with inhalative volumes for 8 h/d defined in the ECHA Guidance at 6.7 m3 for base level activity and 10m3 for light activity.
Corrected NOAEC(systemic-inhalation) = NOAEL(oral-rat)* (1 / sRV(rat)) * ((ABS(oral-rat) / ABS(inhalation-human))) * (sRV(human)/ wRV)
Where ABS = Absorption, sRV = standard Respiratory Volume, and wRV = worker Respiratory Volume. Absorptions by inhalation and oral route are not known, therefore it was considered that oral absorption in the rat was 50% less effective than the human absorption by inhalation in accordance with ECHA Guidance.
Corrected NOAEC(systemic-inhalation) = NOAEL(oral-rat)* (1 / sRV(rat)) * ((ABS(oral-rat) / ABS(inhalation-human))) * (sRV(human)/ wRV)
Corrected NOAEC(systemic-inhalation) = NOAEL(oral-rat)* (1 / sRV(rat)) * 0.5 * (sRV(human)/ wRV)
Corrected NOAEC(systemic-inhalation) = 60 mg/kg bw * (1 / 0.38 m3/kg) * 0.5 * (6.7 m3/ 10 m3)
Corrected NOAEC(systemic-inhalation) = 52.89 mg/m3
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- ECHA REACH Guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 5
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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:
- 0.6 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
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 60 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
In accordance with ECHA Guidance, in order to derive DNEL for the dermal route for systemic effects from an EOGRTS by the oral route, a conversion must be made in order to take into account the differences between the routes.
Corrected NOAEL(systemic-dermal) = NOAEL(oral-rat)* ((ABS(oral-rat) / ABS(dermal-rat)))
Absorptions by dermal and oral routes are not known. On the assumption that, in general, dermal absorption will not be higher than oral absorption, no default factor should be introduced when performing oral-to-dermal extrapolation.
Corrected NOAEL(systemic-dermal) = NOAEL(oral-rat)* ((ABS(dermal-rat) / ABS(oral-human)))
Corrected NOAEL(systemic-dermal) = NOAEL(oral-rat)* 1
Corrected NOAEL(systemic-dermal) = 60 mg/kg bw/day * 1
Corrected NOAEL(systemic-dermal) = 60 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 5
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 40 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Dose descriptor starting point:
- NOAEL
- Value:
- 2 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
LD0 derived from the acute dermal toxicity study has been considered as equivalent to a NOAEL. No systemic or local effects were observed during the acute dermal toxicity study performed on rats. In order to derive DNELs for the dermal route from an acute dermal toxicity study, no conversion is required for the systemic exposure.
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 5
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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:
- no hazard identified
Additional information - workers
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.52 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):
- 50
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 26.09 mg/m³
- Explanation for the modification of the dose descriptor starting point:
As the NOAEL was obtained on rats using the oral route, it must be corrected for an inhalation exposure of the general population, taking into account that the general population is considered as being exposed 24 h/d. A sRV(rat) of 1.15 m3/kg is used in order to consider this 24 h/d exposure.
Corrected NOAEC(systemic-inhalation) = NOAEL(oral-rat)* (1 / sRV(rat)) * ((ABS(oral-rat) / ABS(inhalation-human)))
Corrected NOAEC(systemic-inhalation) = NOAEL(oral-rat)* (1 / sRV(rat)) * 0.5
Corrected NOAEC(systemic-inhalation) = 60 mg/kg bw * (1 / 1.15 m3/kg) * 0.5
Corrected NOAEC(systemic-inhalation) = 26.09 mg/m3
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- ECHA REACH Guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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:
- 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
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 60 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
In accordance with ECHA Guidance, in order to derive DNEL for the dermal route for systemic effects from an EOGRTS by the oral route, a conversion must be made in order to take into account the differences between the routes.
Corrected NOAEL(systemic-dermal) = NOAEL(oral-rat)* ((ABS(oral-rat) / ABS(dermal-rat)))
Absorptions by dermal and oral routes are not known. On the assumption that, in general, dermal absorption will not be higher than oral absorption, no default factor should be introduced when performing oral-to-dermal extrapolation.
Corrected NOAEL(systemic-dermal) = NOAEL(oral-rat)* ((ABS(dermal-rat) / ABS(oral-human)))
Corrected NOAEL(systemic-dermal) = NOAEL(oral-rat)* 1
Corrected NOAEL(systemic-dermal) = 60 mg/kg bw/day * 1
Corrected NOAEL(systemic-dermal) = 60 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 20 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Dose descriptor starting point:
- NOAEL
- Value:
- 2 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
LD0 derived from the acute dermal toxicity study has been considered as equivalent to a NOAEL. No systemic or local effects were observed during the acute dermal toxicity study performed on rats. In order to derive DNELs for the dermal route from an acute dermal toxicity study, no conversion is required for the systemic exposure.
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
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:
- 0.3 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:
- 60 mg/kg bw/day
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.25 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
- DNEL extrapolated from long term DNEL
- Dose descriptor starting point:
- NOAEL
- Value:
- 125 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
Adverse systemic effects were observed during the key study performed at up to 2,000 mg/kg bw and it is therefore not possible to derive a LD0. It is proposed to use for the calculation the value obtained during the reliable Combined Repeated Dose & Reproduction Toxicity study as its duration (subacute) is the closest to an acute exposure.
- AF for dose response relationship:
- 1
- Justification:
- ECHA REACH Guidance
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to Humans
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA REACH Guidance
- AF for intraspecies differences:
- 10
- Justification:
- ECHA REACH Guidance
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA REACH Guidance
- AF for remaining uncertainties:
- 1
- Justification:
- ECHA REACH Guidance
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
There is limited exposure of the substance as such to the general public.
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.