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Diss Factsheets
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EC number: 235-795-5 | CAS number: 12738-64-6
- 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
Basic toxicokinetics
Administrative data
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- High reliability as from EU scientific Committee (EFSA and RAC)
Data source
Materials and methods
Results and discussion
Applicant's summary and conclusion
- Conclusions:
- It is estimated that gastrointestinal absorption of non-hydrolysed or partly hydrolysed sucrose benzoate will not take place. However, some absorption of the mono-esters generated by hydrolysis in the gastrointestinal tract cannot be excluded, whereas 100% absorption of liberated benzoic acid/benzoate and sucrose can be anticipated.
- Executive summary:
Oral absorption and metabolism
No data on sucrose benzoate is available.
For sucrose esters of fatty acids* EFSA (2004) found that in humans after oral exposure 20-30% of single doses were retrieved as intact esters from the faeces after 48 hours, whereas the total human faecal excretion of intact sucrose esters after 5 daily treatments was 17%. A high rate of hydrolysis occurred in the gastrointestinal tract, in accordance with the finding that more than 50% of sucrose esters were hydrolysed within 5 hours in cultures of the human intestinal microflora. However, degradation of various sucrose esters of fatty acids in gastric juice was found to be limited. Metabolic studies in vitro and studies in rats, dogs and humans show that these esters* are extensively hydrolysed in the gastrointestinal tract into well-known food constituents prior to absorption. Only small amounts of intact monoesters are absorbed, and incompletely hydrolysed sucrose esters appear to be excreted in the faeces. Studies using radiolabelled sucrose esters indicate that it is unlikely that di- and higher esters are absorbed intact. There is no evidence of tissue accumulation of the absorbed monoesters as the absorbed monoesters were completely metabolised to carbon dioxide or integrated into other endogenous constituents.
(*Sucrose esters of fatty acids consist of a mixture of mono- di- and triesters of sucrose with food fatty acids (mainly C14:0, C16:0, C18:0 and/or C18:1 fatty acids)).
This is in concordance with CIR (2016) that concluded “Generally in rats, dogs, and monkeys, sucrose esters were not found in whole blood or plasma following oral administration”.
In relation to benzoic acid/benzoate (formed by hydrolysis iof sucrose benzoate) the gastrointestinal absorption is rapid and virtually complete in humans, rats, dogs, and hamsters (ECHA/RAC 2012).
From these data it is estimated that gastrointestinal absorption of non-hydrolysed or partly hydrolysed sucrose benzoate will not take place. However, some absorption of the mono-esters generated by hydrolysis in the gastrointestinal tract cannot be excluded, whereas 100% absorption of liberated benzoic acid/benzoate and sucrose can be anticipated.
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