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EC number: 211-492-3 | CAS number: 652-67-5
- 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
Acute/short term exposure
DNEL related information
Local effects
Acute/short term exposure
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 697.29 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 24
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
DNEL related information
Workers - Hazard for the eyes
Additional information - workers
Worker-DNEL long-term dermal route
The substance is considered as a non-hazardous substance which has no local toxicity and CMR concern. Therefore, the long term systemic toxicity is regarded as the leading health effect.
For isosorbide, a valid study addressing repeated dose toxicity is available:
In an oral (feed) 90-day subchronic toxicity study in rats according to OECD TG 408 (Repeated Dose 90-Day Oral Toxicity in Rodents), the No Observed Effect Level (NOEL) was established at 12500 ppm (corresponding to 748 mg/kg/day in males and 937 mg/kg/day in females) and the No Observed Adverse Effect Level (NOAEL) was set at 50,000 ppm (corresponding to 3,347 mg /kg/day in malesand 3,970 mg/kg/day in females).
Data from this study was considered a suitable dose descriptor for derivation of respective DNELs, and the defined NOAEL was chosen as the point of departure for derivation of the dermal long term systemic DNEL by route to route extrapolation. Based on the physical state of isosorbide, which has low vapour pressure (between 0.0057 and 0.0079 Pa) and is used in a granular form, dermal exposure is considered to be the relevant route, whereas inhalation route is considered as insignificant exposure.
NOAEL= 3,347 mg /kg/day was selected to derive DNELs.
There is no toxicokinetics study availe for isosorbide and only limited pharmacokinetic data were provided from the production of LAB 3822 (a mixture) by read-across approach. Hence there is no absorption data by either route.
Isosorbide is highly bioavaile and high levelof the systemic exposure was clearly demonstrated in a reproductive toxicity study and suggests no barriers to oral absorption but information from acute dermal toxicity (LD50>2,000 mg/kg, no effects) indicates low dermal absorption and no irritant effects on the skin.
Due to the lack on further specific route information, it is assumed that the bioavaiility across the skin is no greater than the oral bioavaiility. Therefore, an oral absorption of 50 % and dermal absorption of 10 % were assumed for isosorbide (CR12, IGHRC 2006).
To derive the long-term systemic dermal DNEL, the oral NOAEL of 3,347 mg /kg/day was converted into a corrected dermal NOAEL of 16,735 mg/kg bw/day according to the procedure recommended in the guidance document (R8, ECHA 2010).
Oral NOAEL =3,347 mg /kg/day; Absorption-oral =50 %;Absorption-dermal =10 %.
Corrected dermal NOAEL=oral NOAEL * (Absorption-oral/ Absorption-dermal)
=3,347* (50/10) = 16,735 mg /kg/day
General Population - Hazard via inhalation route
Systemic effects
Acute/short term exposure
DNEL related information
Local effects
Acute/short term exposure
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 418.38 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 40
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
DNEL related information
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 83.68 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 40
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
DNEL related information
General Population - Hazard for the eyes
Additional information - General Population
General Population-DNEL long-term oral and dermal routes
The substance is considered as a non-hazardous substance which has no local toxicity and CMR concern. Therefore, the long term systemic toxicity is regarded as the leading health effect.
For isosorbide, a valid study addressing repeated dose toxicity is available:
In an oral (feed) 90-day subchronic toxicity study in rats according to OECD TG 408 (Repeated Dose 90-Day Oral Toxicity in Rodents), the No Observed Effect Level (NOEL) was established at 12,500 ppm (corresponding to 748 mg/kg/day in males and 937 mg/kg/day in females) and the No Observed Adverse Effect Level (NOAEL) was set at 50,000 ppm (corresponding to 3347 mg /kg/day in malesand 3,970 mg/kg/day in females).
Data from this study was considered a suitable dose descriptor for derivation of respective DNELs, and the defined NOAEL was chosen as the point of departure for derivation of the dermal long term systemic DNEL by route to route extrapolation. Based on the physical state of isosorbide, which has low vapour pressure (between 0.0057 and 0.0079 Pa) and is used in a granular form, oral and dermal exposure are considered to be the relevant routes, whereas inhalation route is considered as insignificant exposure.
NOAEL= 3,347 mg /kg/day was selected to derive both oral and dermal DNELs
There is no toxicokinetics study availe for isosorbide and only limited pharmacokinetic data were provided from the production of LAB 3822 (a mixture) by read-across approach. Hence there is no absorption data by either route.
Isosorbide is highly bioavailable and high levelof the systemic exposure was clearly demonstrated in a reproductive toxicity study and suggests no barriers to oral absorption but information from acute dermal toxicity (LD50>2000 mg/kg, no effects) indicates low dermal absorption and no irritant effects on the skin.
Due to the lack on further specific route information, it is assumed that the bioavailability across the skin is no greater than the oral bioavailability. Therefore an oral absorption of 50 % and dermal absorption of 10 % were assumed for isosorbide (CR12, IGHRC 2006).
To derive the long-term systemic dermal DNEL, the oral NOAEL of 3347 mg /kg/day was converted into a corrected dermal NOAEL of 16,735 mg/kg bw/day according to the procedure recommended in the guidance document (R8, ECHA 2010).
Oral NOAEL =3,347 mg /kg/day; Absorption-oral =50 %;Absorption-dermal =10 %.
Corrected dermal NOAEL=oral NOAEL * (Absorption-oral/ Absorption-dermal)
=3347* (50/10) = 16,735 mg /kg/dayInformation 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.
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