Registration Dossier
Registration Dossier
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: 270-337-8 | CAS number: 68425-17-2
- 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

Endpoint summary
Administrative data
Description of key information
According to Annex VIII, column 2, a 28-day study is not required as a suitable (sub-)chronic study is available.
In a key 13-week gavage study conducted with Lycasin 80/55, a NOAEL value of 4.95 g/kg body weight/day (limit test, actual ingested) was derived for male and female dogs (Virat, 1982).
One (1) key study and 1 supporting study for long term repeated dose toxicity (>=12 months) were identified. In a 52-week repeated dose toxicity study with Malbit® (87% maltitol, 5% sorbitol, 6% maltotriitol, dry substance), the NOAEL of 4.5 g/kg body weight/day was identified for male and female rats (Conz and Fumero, 1989).
In a 24-month drinking water study conducted with Lycasin 80/55 (7.0% sorbitol, 52.5% maltitol, 22.5% tri- to hexasaccharides, and 17.5% higher-order hydrogenated saccharides), a NOAEL value of 18% in drinking water (limit test, nominal) was derived for male and female rats (Modderman, 1993; Leroy and Dupas, 1984).
Exposure by inhalation or dermal routes are not considered the most relevant route of exposure; no inhalation or dermal studies were identified.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 4 500 mg/kg bw/day
Additional information
Metabolic data demonstrate that the notifiable substance (Lycasin® 80/55), as well as the read-across substances (maltose, maltitol, sorbitol, wheat glucose syrup (WGS), and dextrin) share a common metabolic pathway as they are converted to D-glucose and/or sorbitol via hydrolysis of their glycosidic linkages by the intestinal brush border carbohydrases. On the basis of their common mono- and disaccharide metabolites, the properties of the notifiable substance, Lycasin® 80/55 is expected to be similar to the read-across substances maltose, sorbitol, maltitol, WGS, and dextrin. Considering this, it is anticipated that exposure to any of the aforementioned saccharides would ultimately result in the formation of D-glucose and/or sorbitol. As such, maltose, sorbitol, maltitol, WGS, and dextrin may be used as appropriate surrogates for the notifiable substance, considering their common metabolic products.
According to Annex VIII, column 2, a 28-day study is not required as a suitable (sub-)chronic study is available.
One key sub-chronic toxicity study was identified. In this study, which was similar in design to OECD testing guideline 409, Lycasin 80/55 at 0 (control), or 4.95 g/kg body weight/day (actual ingested) was administered by gavage to Beagle dogs for a period of 13 weeks (Virat, 1982). Four (4) animals per sex were included in each group. Endpoints assessed included clinical signs, body weight, food consumption, ophthalmoscopic examination, haematology, clinical chemistry, urinalysis, gross pathology, and histopathology. The occurrence of diarrhea, a slight increase in the level of circulating triglycerides in 3 female dogs, and a minimal ectasia in the renal tubules were reported. The authors considered these observations to be physiological, in relation to the high amount of hydrogenated sugar provided by the treatment. NOAEL values were not reported by the study authors. Review of the study data suggested that a NOAEL of 4.95 g/kg body weight/day (actual ingested) can be considered in both male and female dogs based on a lack of toxicity.
One (1) key study and 1 supporting study for long term repeated dose toxicity (>=12 months) were identified. In the key long term repeated dose toxicity study, Malbit® (87% maltitol, 5% sorbitol, 6% maltotriitol, dry substance) was evaluated in a 52-week study in rats (Conz and Fumero, 1989). This GLP study was similar in design to OECD test guideline 453. Malbit® was administered via the diet at 0 (control), 0.5, 1.5, or 4.5 g/kg body weight/day to Sprague-Dawley rats (20 rats/sex/group) for 52 weeks. Endpoints assessed included clinical signs, body weight, food consumption, ophthalmoscopic examination, haematology, clinical chemistry, urinalysis, gross pathology, and histopathology. There were no differences in mortality, ophthalmoscopical examination, body weight, food consumption, behaviour, hematology, or urinalysis. At blood chemistry only, a few minor functional modifications emerged mainly in males at 26 and/or 51 weeks of treatment, without morphological-related changes. These were a slight increase, not dosage-related, in mean creatinine values in all treated male groups (51 weeks) with individual values within the norm, a slight reduction in the highest dosage treated males, of total, free and esterified cholesterol accompanied by a reduction in the NEFA values (26 and 51 weeks); a slight increase in the highest dosage group of females, in the alpha lipoprotein fraction (serum lipoprotein electrophoresis) was also seen at 51 weeks when this examination was performed. At post-mortem examinations, no modifications related to treatment were seen in particular, no compound-related dilatations of cecum and colon diameter were seen, and no compound-related morphological changes of the gastrointestinal tract were found. In conclusion, under the experimental conditions applied, the test substance was well tolerated when administered into the diet for 52 weeks to Sprague Dawley CD (SD) BR rats up to and including the highest dose level tested of 4.5 g/kg body weight/day. Based on the results, a NOAEL of 4.5 g/kg body weight/day was derived.
The supporting study was similar in design to OECD testing guideline 452 (Modderman, 1993; Leroy and Dupas, 1984). Lycasin® 80/55 (7.0% sorbitol, 52.5% maltitol, 22.5% tri- to hexasaccharides, and 17.5% higher-order hydrogenated saccharides) at 0 (control) or 18% in water was administered in drinking water to Sprague-Dawley rats for a period of 24 months. Fifty (50) animals per sex were included in each group. Endpoints assessed included clinical signs, body weight, water consumption, haematology, clinical chemistry, urinalysis, gross pathology, and histopathology. Diarrhea was observed in early stages in dosed group, which disappeared by the fourth week and mean body weight was significantly lower in the dosed group in the early stage of dosing period. In addition, food consumption was significantly lower and beverage consumption was higher in the dosed group. A significant decrease in the concentration of electrolytes in the urinalysis parameter and a significant increase in the relative cecum weight of the dosed group were observed. The authors commented that these observations have been observed commonly in feeding studies involving slowly digestible carbohydrates and polyols and have been correlated with adaptive responses to the low digestibility of the test substances. The authors further commented that these changes have been not correlated to any other specific toxicological characteristic of these substances. NOAEL values were not reported by the study authors. Review of the study data suggested that a NOAEL value of 18% in drinking water can be considered in male and female rats, based on the lack of toxicological effects.
Justification for classification or non-classification
The notifiable substance did not exhibit significant toxic effects arising from a repeated exposure. As a result, the substance does not meet the criteria for classification according to Regulation (EC) No 1272/2008, Annex I section 3.9.
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.