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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 203-797-5 | CAS number: 110-73-6
- 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:
- 0.2 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):
- 225
- Modified dose descriptor starting point:
- LOAEC
- Value:
- 44 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The relevant endpoint is the oral LOAEL of 50 mg/kg bw/d from the screening study. This is extrapolated to an inhalation LOAEC of 44 mg/m3 following correction for breathing rate and activity (/0.38 * 0.67) and for oral absorption of 50% and inhalation absorption of 100%.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from a sub-acute study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not required (accounted for in route-route extrapolation)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 5
- Justification:
- Default value (workers)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.2 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):
- 37.5
- Modified dose descriptor starting point:
- LOAEC
- Value:
- 44 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The relevant endpoint is the oral LOAEL of 50 mg/kg bw/d from the screening study. This is extrapolated to an inhalation LOAEC of 44 mg/m3 following correction for breathing rate and activity (/0.38 * 0.67) and for oral absorption of 50% and inhalation absorption of 100%.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not required (accounted for in route-route extrapolation)
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 5
- Justification:
- Default value (workers)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.06 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):
- 900
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Correction of the starting point (a LOAEL of 50 mg/kg bw/d from an oral study) is not required as oral and dermal absorption are assumed to be comparable.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from a sub-acute study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Use of a rat study
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 5
- Justification:
- Default value (workers)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.33 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):
- 150
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Repeated exposure information via the dermal application route was not available. A subacute endpoint was derived from an orally administered study (30 day and 90day exposure in drinking water), for the subacute duration only. The NOAEL was calculated based on a ppm dose concentration, overall intake and mean bodyweight. The NOAEL estimate was 40 mg/kg bw/day. Another endpoint was derived from a reproductive/developmental toxicity screening test. THe LOAEL from this study was 50 mg/kg bw/day. This was used as the starting point for the derivation of the DNEL by route-to route extrapolation based on the precautionary principle. The local effects of dermal corrosion may be mitigated by use of RMMs, but the overall toxicity profile for 2-ethylaminoethanol suggests short-term peak exposure effects and local corrosivity effects should be protected by a short term DNEL.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Use of a rat study
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 5
- Justification:
- Default value (workers)
- AF for the quality of the whole database:
- 1
- Justification:
- Default value
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - workers
The substance is corrosive, however quantitative endpoints are not available and local dermal and inhalation DNELs are not derived. Inhalation and dermal exposure to the substance should be minimised though the use of engineering controls and protective equipment.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.05 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):
- 450
- Modified dose descriptor starting point:
- LOAEC
- Value:
- 22 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The relevant endpoint is the oral LOAEL of 50 mg/kg bw/d from the screening study. This is extrapolated to an inhalation LOAEC of 22 mg/m3 following correction for breathing rate (/1.15) and for oral absorption of 50% and inhalation absorption of 100%.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from a sub-acute study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not required (accounted for in route-route extrapolation)
- 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:
- default value
- AF for remaining uncertainties:
- 1
- Justification:
- default value
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.3 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:
- LOAEC
- Value:
- 22 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The relevant endpoint is the oral LOAEL of 50 mg/kg bw/d from the screening study. This is extrapolated to an inhalation LOAEC of 22 mg/m3 following correction for breathing rate (/1.15) and for oral absorption of 50% and inhalation absorption of 100%.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Not required (accounted for in route-route extrapolation)
- 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:
- default value
- AF for remaining uncertainties:
- 1
- Justification:
- default value
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.03 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):
- 1 800
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Correction of the starting point (a LOAEL of 50 mg/kg bw/d from an oral study) is not required as oral and dermal absorption are assumed to be comparable.
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Extrapolation from a sub-acute study to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default value (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:
- default value
- AF for remaining uncertainties:
- 1
- Justification:
- default value
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.2 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):
- 300
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Repeated exposure information via the dermal application route was not available. A valid subacute endpoint was derived from an orally administered study (30 day and 90day exposure in drinking water), for the subacute duration only. The NOAEL was calculated based on a ppm dose concentration, overall intake and mean bodyweight. The NOAEL estimate was 40 mg/kg bw/day. A more reliable LOAEL of 50 mg/kg bw/day was obtained from a reproductive/developmental toxicity study was used as the starting point for the derivation of the DNEL by route-to route extrapolation based on the precautionary principle. This was used as the starting point for the derivation of the DNEL by route-to route extrapolation based on the precautionary principle. Since no local effects or short-term peak exposure effects were indicated, the long term DNEL is expected to be protective for short term exposure also.
- AF for dose response relationship:
- 3
- Justification:
- LOAEL used as starting point for DNEL derivation
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default value for rats
- AF for other interspecies differences:
- 2.5
- Justification:
- default value
- AF for intraspecies differences:
- 10
- Justification:
- default value
- AF for the quality of the whole database:
- 1
- Justification:
- default value
- AF for remaining uncertainties:
- 1
- Justification:
- default value
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.03 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):
- 1 800
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Not required: starting point is a LOAEL from an oral study
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from subacute to chronic exposure
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default value (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:
- default value
- AF for remaining uncertainties:
- 1
- Justification:
- default value
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.2 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):
- 300
- DNEL extrapolated from long term DNEL
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Not required: starting point is a LOAEL from an oral study
- AF for dose response relationship:
- 3
- Justification:
- Use of a LOAEL
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default value (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:
- default value
- AF for remaining uncertainties:
- 1
- Justification:
- default value
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - General Population
The substance is corrosive, however quantitative endpoints are not available and local dermal and inhalation DNELs are not derived. Inhalation and dermal exposure to high concentrations of the substance (sufficient to cause local effects) should be avoided.
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.