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EC number: 213-235-0 | CAS number: 931-40-8
- 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
Acute/short term exposure
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 41.75 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- other: according to ECETOC Technical Report #86.
- Overall assessment factor (AF):
- 3
- Dose descriptor:
- other: NOAEC: 125.25 mg/m³
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- Since the most sensitive endpoint was based on an adaptive response and glycerol is not expected to accumulate, a duration adjustment to chronic exposure was not used.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for local effects
- AF for other interspecies differences:
- 1
- AF for intraspecies differences:
- 3
- Justification:
- according to ECETOC Technical Report #86.
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
- Most sensitive endpoint:
- acute toxicity
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
Acute
/ short-term exposure (systemic and local effects):
- An acute dermal toxicity test was performed in rabbits. None of the
rabbits died at 3000 mg/kg, the highest dose level tested. The LD50 is
greater than 3000 mg/kg bw/day. Therefore, a DNEL for acute dermal
toxicity is not quantifiable.
- An acute inhalation toxicity test was performed in rats. None of the
rats died at 5.6 mg/L, the only dose tested. The LC50 value was greater
than 5.6 mg/L. Therefore, a DNEL or acute inhalation toxicity is not
quantifiable.
- Based on the available data and according to the criteria laid down in
the DSD and CLP Regulation (EC) 1272/2008, glycerine carbonate is
neither classified for skin irritation/corrosion nor for eye damage. No
DNEL was derived based on the available data.
Long-term exposure (systemic effects):
- Dermal: No-threshold effect and/or no dose-response information available for systemic effects neither from glycerine carbonate nor from the read-across substance glycerol. The long-term dermal DNEL was based on no effects in the rabbit dermal subchronic (45 wk) toxicity study. The rat subchronic study identified a NOAEL of 4580 mg/kg, based on cloudy swelling and hypertrophy of liver, but this is considered to be an adaptive response to high-dose administration of a normal component of intermediate metabolism, and of questionable relevance for exposure by the dermal route of exposure.
- Inhalation: No-threshold effect and/or no dose-response information available for systemic effects neither from glycerine carbonate nor from the read-across substance glycerol.
Long-term exposure (local effects):
- Inhalation: No long term toxicity studies via the inhalation route are available for glycerine carbonate. However, a systemic inhalation NOAEC of 167 mg/m³ was obtained for the read-across substance glycerol in a 90 day repeated dose toxicity study in rats. A conversion factor of 0.75 was used to convert from 6 to 8 hours of exposure per day. Therefore, the dose descriptor starting point = 125.25 mg/m³ (167 mg/m³ x (6 hours/8 hours)).
With an overall assessment factor of 3 (intraspecies differences according to ECETOC Technical Report #86.), the long-term DNEL, inhalation for local effects of 125.25 mg/m³/3 = 41.75 mg/m³ is derived.
General Population - Hazard via inhalation route
Systemic effects
Acute/short term exposure
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 8.35 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- other: according to ECETOC Technical Report #86.
- Overall assessment factor (AF):
- 5
- Dose descriptor:
- other: NOAEC 41.75 mg/m³
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- Since the most sensitive endpoint was based on an adaptive response and glycerol is not expected to accumulate, a duration adjustment to chronic exposure was not used.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for local effects
- AF for other interspecies differences:
- 1
- AF for intraspecies differences:
- 5
- Justification:
- according to ECETOC Technical Report #86.
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
- Most sensitive endpoint:
- acute toxicity
DNEL related information
Local effects
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
- Most sensitive endpoint:
- acute toxicity
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 229 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: according to ECETOC Technical Report #86.
- Overall assessment factor (AF):
- 20
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 4 580 mg/kg bw/day
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Rats to humans
- AF for other interspecies differences:
- 1
- Justification:
- according to ECETOC Technical Report #86.
- AF for intraspecies differences:
- 5
- Justification:
- according to ECETOC Technical Report #86.
- 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
Acute / short-term exposure (systemic and local effects):
- An acute dermal toxicity test was performed in rabbits. None of the rabbits died at 3000 mg/kg, the highest dose level tested. The LD50 is greater than 3000 mg/kg bw/day. Therefore, a DNEL for acute dermal toxicity is not quantifiable.
- An acute oral toxicity test was performed in rats. The LD50 was determined to be greater than 5000 mg/kg bw/day. No acute DNEL was derived based on the available data.
- An acute inhalation toxicity test was performed in rats. None of the rats died at 5.6 mg/L, the only dose tested. The LC50 value was greater than 5.6 mg/L. Therefore, a DNEL or acute inhalation toxicity is not quantifiable.
- Based on the available data and according to the criteria laid down in the DSD and CLP Regulation (EC) 1272/2008, glycerine carbonate is neither classified for skin irritation/corrosion nor for eye damage. No DNEL was derived based on the available data.
Long-term exposure (systemic effects):
- Dermal: No-threshold effect and/or no dose-response information available for systemic effects neither from glycerine carbonate nor from the read-across substance glycerol. The long-term dermal DNEL was based on no effects in the rabbit dermal subchronic (45 wk) toxicity study. The rat subchronic study identified a NOAEL of 4580 mg/kg, based on cloudy swelling and hypertrophy of liver, but this is considered to be an adaptive response to high-dose administration of a normal component of intermediate metabolism, and of questionable relevance for exposure by the dermal route of exposure.
- Inhalation: No-threshold effect and/or no dose-response information available for systemic effects neither from glycerine carbonate nor from the read-across substance glycerol.
- Oral: The long-term oral DNEL was based upon on cloudy swelling and hypertrophy of liver in the rat subchronic study (NOAEL 4580 mg/kg), which is considered to be an adaptive response to high-dose administration of a normal component of intermediate metabolism. There were no effects on tumour response or inflammation in a chronic bioassay. With an overall assessment factor of 20 (x4 for interspecies differences and x5 for intraspecies differences), the long-term DNEL, inhalation for systemic effects of 4580 mg/kg/20 = 242 mg/kg is derived.
Long-term exposure (local effects):
- No long term toxicity studies via the inhalation route are available for glycerine carbonate. However, a systemic inhalation NOAEC of 167 mg/m³ was obtained for glycerol in a 90 day repeated dose study on rats. A conversion factor of 0.25 was used to convert from 6 to 24 hours of exposure per day. Therefore, the dose descriptor starting point =41.75 mg/m³ (167 mg/m³ x (6 hours/24 hours)).
With an overall assessment factor of 5 (intraspecies differences), the long-term DNEL, inhalation for systemic effects of 41.75 mg/m³/5 = 8.35 mg/m³ is derived.
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