Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 203-225-4 | CAS number: 104-67-6
- 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:
- 19 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:
- 1 423 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- For potential inhalation exposure, route-to-route extrapolation from the oral NOAEL value (1000 mg/kg bw/d) of gamma-caprolactone (aliphatic lactone used in a read-across approach) was performed. In the absence of specific data for both the starting route (oral) and the end route (inhalation), worst case assumptions have to be made. It was assumed that a limited absorption occurs by the oral route, leading to a low (conservative) internal NOAEL. To secure a conservative external NOAEL, a maximum absorption should be assumed for the inhalation route (i.e.; 100%) leading to a low external NOAEL. Thus, in the case of oral-to- inhalation extrapolation, it is proposed to include a default factor of 2, i.e. the absorption percentage by oral route is half that of the inhalation absorption as suggested on page 19 of Guidance Document, Chapter R.8. Finally, to convert the oral NOAEL into inhalatory NOAEC, a rat default respiratory volume was used corresponding to the daily duration of human exposure (sRVrat: 0.38 m3/kg bw/8 h). For workers a correction was added for the difference between respiratory rates under standard conditions (sRVhuman: 6.7 m3 for an 8-h exposure period) and under conditions of light activity (wRV: 10 m3 for an 8-h exposure period). Thus, for gamma-caprolactone, the corrected dose descriptor for inhalation is 882 mg/m3 for workers. Then, a correction factor based on the ratio between the molecular mass of gamma-undecalactone (184 g/ml) and gamma-caprolactone (114 g/mol) was applied to extrapolate the corrected starting point for gamma-undecalactone.
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic extrapolation as DNEL is based on 28-day study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for inhalation route
- AF for other interspecies differences:
- 2.5
- Justification:
- Remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- Worker
- AF for the quality of the whole database:
- 1
- 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:
- 5.38 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:
- NOAEL
- Value:
- 1 614 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- For potential dermal exposure, route-to-route extrapolation from the oral NOAEL value was performed. In the absence of specific data and 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 (see Guidance Document, Chapter R.8, pp 19). Thus, for gamma-Caprolactone, the corrected dose descriptor for dermal route is 1000 mg/kg bw/day for workers. Then, a correction factor based on the ratio between the molecular mass of gamma-undecalactone (184 g/ml) and gamma-caprolactone (114 g/mol) was applied to extrapolate the corrected starting point for gamma-undecalactone.
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic extrapolation as DNEL is based on 28-day study
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rat
- AF for other interspecies differences:
- 2.5
- Justification:
- Remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- Worker
- AF for the quality of the whole database:
- 1
- 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
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:
- 4.68 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:
- 702 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- For potential inhalation exposure, route-to-route extrapolation from the oral NOAEL value was performed. In the absence of specific data for both the starting route (oral) and the end route (inhalation), worst case assumptions have to be made. It was assumed that a limited absorption occurs by the oral route, leading to a low (conservative) internal NOAEL. To secure a conservative external NOAEL a maximum absorption should be assumed for the inhalation route (i.e.; 100%) leading to a low external NOAEL. Thus, in the case of oral-to- inhalation extrapolation, it is proposed to include a default factor of 2, i.e. the absorption percentage by oral route is half that of the inhalation absorption as suggested on page 19 of Guidance Document, Chapter R.8. Finally, to convert the oral NOAEL into inhalatory NOAEC, a rat default respiratory volume was used corresponding to the daily duration of human exposure (sRVrat: 1.15 m3/kg bw/24 h). Thus, for gamma-caprolactone, the corrected dose descriptor for inhalation is 435 mg/m3 for the general population. Then, a correction factor based on the ratio between the molecular mass of gamma-undecalactone (184 g/ml) and gamma-caprolactone (114 g/mol) was applied to extrapolate the corrected starting point for gamma-undecalactone.
- AF for dose response relationship:
- 1
- Justification:
- NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic extrapolation as DNEL is based on 28-day study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for inhalation route
- 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
- 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:
- 2.7 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:
- 1 614 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- For potential dermal exposure, route-to-route extrapolation from the oral NOAEL value was performed. In the absence of specific data and 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 (see Guidance Document, Chapter R.8, pp 19). Thus, for gamma-caprolactone, the corrected dose descriptor for dermal route is 1000 mg/kg bw/day for the general population. Then, a correction factor based on the ratio between the molecular mass of gamma-undecalactone (184 g/ml) and gamma-caprolactone (114 g/mol) was applied to extrapolate the corrected starting point for gamma-undecalactone.
- AF for dose response relationship:
- 1
- Justification:
- NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic extrapolation as DNEL is based on 28-day study
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rat
- 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
- 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
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.7 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:
- 1 614 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- The oral NOAEL value was used as the dose descriptor for DNEL long-term for oral route derivation. However, a correction factor based on the ratio between the molecular mass of gamma-undecalactone (184 g/ml) and gamma-caprolactone (114 g/mol) was applied to extrapolate the corrected starting point for gamma-undecalactone.
- AF for dose response relationship:
- 1
- Justification:
- NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic extrapolation as DNEL is based on 28-day study
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rat
- 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
- 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:
- no hazard identified
Additional information - General Population
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.