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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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Except data obtained from the scientific literature, the studies performed either on Isosorbide (LAB 3085) or on LAB 3822 were performed according OECD good laboratory practices.
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Data source
Reference
- Reference Type:
- other: analysis by an expert
- Title:
- Analysis of data available for Isosorbide risk assessment
- Author:
- Pf D.Marzin
- Report date:
- 2010
Materials and methods
Results and discussion
Results (fetuses)
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- Isosorbide was tested for toxicokinetics and toxicology either as Isosorbide form or its precursor LAB 3822, which was demonstrated as quickly and completely metabolized into Isosorbide and into capric and caprylic acids.
After administration of LAB 3822 animals are exposed to Isosorbide. The level of exposure is proportional to the dose. Exposure to isosorbide is higher when administered alone than when it is administered as LAB 3822, but the isosorbide dose equivalent administered at the maximum dose of LAB3822 (0.67 mg/kg) is largely lower that when it was administered alone (2g/kg). The T1/2 (plasma and urine) and Tmax (plasma) of isosorbide was not different when isosorbide is administered as LAB3822 or as Isosorbide itself. In both cases males are more exposed than females. The excretion of isosorbide is almost in the urine as unchanged isosorbide. The metabolism and the pharmacokinetics were similar in all the species studied including human.
The acute toxicity is low in all the species tested including human by all the route tested including intravenous route. With such a low acute toxicity, Isosorbide need no classification. The symptoms were the same in all species including human and are limited, at high doses (> 10g/kg) to gastro-intestinal effects: nausea, vomiting and diarrhoea.
In the repeated toxicity doses isosorbide was tested in the rat in GLP studies up to 13 weeks by oral route by addition in the diet. No toxic effects were observed and the maximum daily doses tested which were the maximum feasible doses (3347 mg/kg/day for the males and 3970 mg/kg/day for the females) are the NOAEL in this species. Data from literature demonstrated that in the rat when administered in the diet at 10% up to 18 months or in the dog at 12g/kg/day up to 52 weeks no toxic effects were demonstrated.
Isosorbide was demonstrated as not irritant for the eye and the skin in vivo in the rabbit and not a skin sensitizer in the mouse in the LLNA test. Under these conditions, Isosorbide need no classification for local tolerance.
Isosorbide demonstrated no genotoxic potential in a battery of 3 in vitro tests able to demonstrate gene mutation in bacteria, gene mutation in mammal cells and clastogenic and aneugenic potential in mammal cells. These results are sufficient and there is no need for complementary data. In the absence of genotoxic potential, there is no need for a classification of Isosorbide.
In the absence of genotoxic potential and of abnormal signs of cells proliferation or hyperplasia in repeat doses toxicity studies there is no need for carcinogenicity studies and there is no need for a classification of Isosorbide.
Reproduction toxicity studies were performed in the rat using LAB 3822 the maximum administered dose was 0.81 g/kg isosorbide equivalent, this dose is weakly lower than the maximum recommended dose in the OECD guideline (1 g/kg/day). However, this study was considered as acceptable because the dose maximum dose tested is close to this maximum recommended dose, Isosorbide is highly bioavailable and high level of the systemic exposure was clearly demonstrated, because isosorbide is not metabolized and this fact explained the high level of systemic exposure and the study was not limited to this limit dose but 3 dose levels were tested and finally at this dose level the results demonstrated clearly the absence of toxicity for the dam and for the foetus. On the other hand data from literature, although limited, confirmed the absence of this type of toxic effects. In the absence of reproductive toxicity potential, there is no need for a classification of Isosorbide.
Due to the use of Isosorbide from several years as a drug, human data are available and demonstrated the good tolerance for long duration of treatment at high doses.
Under these considerations, the available data are sufficient to conclude that Isosorbide presents a very weak toxicity level that no complementary studies are needed for risk assessment and that isosorbide need no classification.
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