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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 227-813-5 | CAS number: 5989-27-5
- 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:
- 66.7 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:
- 5 000 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Under the test conditions, the LOAEL for beagle dogs was considered to be 1000 mg/kg bw/day, respectively, based on the increased absolute and relative female kidney weight and relative male kidney weight. D-limonene has the same absorption rate between oral and inhalation routes (See section 7.1) therefore no correction factor was applied for differences in absorption between oral and inhalation routes. To convert the oral LOAEL into inhalatory LOAEC, a dog default respiratory volume was used corresponding to the daily duration of human exposure (sRVdog: 0.134 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, the corrected dose descriptor for inhalation is: LOAEC (mg/m3) = 1000 / 0.134 x 6.7/10 = 5000 mg/m3 for workers.
- AF for dose response relationship:
- 3
- Justification:
- Default factor to convert a LOAEC into a NOAEC
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic extrapolation
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for oral to inhalation extrapolation
- AF for other interspecies differences:
- 2.5
- Justification:
- Toxicodynamic and toxicokinetic remaining differencies
- AF for intraspecies differences:
- 5
- Justification:
- Default factor for workers
- AF for the quality of the whole database:
- 1
- Justification:
- Appropriate database
- AF for remaining uncertainties:
- 1
- Justification:
- None
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:
- 9.5 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):
- 105
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- No additional factor is needed when performing oral to dermal extrapolation
- AF for dose response relationship:
- 3
- Justification:
- Default factor to convert a LOAEL into a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic extrapolation
- AF for interspecies differences (allometric scaling):
- 1.4
- Justification:
- Allometric scaling from dog to human
- AF for other interspecies differences:
- 2.5
- Justification:
- Toxicodynamic and toxicokinetic remaining differencies
- AF for intraspecies differences:
- 5
- Justification:
- Default factor for workers
- AF for the quality of the whole database:
- 1
- Justification:
- Appropriate database
- AF for remaining uncertainties:
- 1
- Justification:
- None
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- medium 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:
- 16.6 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:
- LOAEC
- Value:
- 2 488 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Under the test conditions, the LOAEL for beagle dogs was considered to be 1000 mg/kg bw/day, respectively, based on the increased absolute and relative female kidney weight and relative male kidney weight. D-limonene has the same absorption rate between oral and inhalation routes (See section 7.1) therefore no correction factor was applied for differences in absorption between oral and inhalation routes. The dog Standard Respiratory Volume (SRV) for 24 h exposure is used to convert the oral LOAEL into an inhalatory LOAEC (sRVdog: 0.402 m3/kg bw/24h). The corrected starting point is thus calculated as follows: corrected inhalatory LOAEC = oral LOAEL x (1/sRVdog); thus corrected inhalation LOAEC for general population = 1000 mg/kg bw/d x (1/0.402 m3/kg bw/d) = 2488 mg/m3
- AF for dose response relationship:
- 3
- Justification:
- Default factor to convert a LOAEC into a NOAEC
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic extrapolation
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for oral to inhalation extrapolation
- AF for other interspecies differences:
- 2.5
- Justification:
- Toxicodynamic and toxicokinetic remaining differencies
- AF for intraspecies differences:
- 10
- Justification:
- Default factor for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Appropriate database
- AF for remaining uncertainties:
- 1
- Justification:
- None
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:
- 4.8 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):
- 210
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- No additional factor is needed when performing oral to dermal extrapolation
- AF for dose response relationship:
- 3
- Justification:
- Default factor to convert a LOAEL into a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic extrapolation
- AF for interspecies differences (allometric scaling):
- 1.4
- Justification:
- Allometric scaling from dog to human
- AF for other interspecies differences:
- 2.5
- Justification:
- Toxicodynamic and toxicokinetic remaining differencies
- AF for intraspecies differences:
- 10
- Justification:
- Default factor for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Appropriate database
- AF for remaining uncertainties:
- 1
- Justification:
- None
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:
- 4.8 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):
- 210
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- No route-to-route extrapolation needed
- AF for dose response relationship:
- 3
- Justification:
- Default factor to convert a LOAEL into a NOAEL
- AF for differences in duration of exposure:
- 2
- Justification:
- Subchronic to chronic extrapolation
- AF for interspecies differences (allometric scaling):
- 1.4
- Justification:
- Allometric scaling from dog to human
- AF for other interspecies differences:
- 2.5
- Justification:
- Toxicodynamic and toxicokinetic remaining differencies
- AF for intraspecies differences:
- 10
- Justification:
- Default factor for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Appropriate database
- AF for remaining uncertainties:
- 1
- Justification:
- None
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.