Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
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: 937-260-8 | CAS number: -
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
Based on the analogue approach justification, the following results on the algal toxicity obtained on Vinasses, residue of fermentation, can be applied to the Vinasses, residue of fermentation, depotassified :
EC50(72h) > 100 mg/L (nominal), EC50 > 56 mg/L (measured) - for growth
NOEC(72h) = 100 mg/L (nominal), NOEC = 56 mg/L (measured) - for growth
Key value for chemical safety assessment
Additional information
One key study is available on Vinasses, residue of fermentation. The toxicity towards aquatic algae was investigated in a study conducted according to the OECD Guideline 201 “Alga, Growth Inhibition Test” (Bouwman, 2010). The freshwater algaePseudokirchneriella subcapitatawas used as test organism and exposed to a nominal concentration of 100 mg/L for 72 h. Based on the TOC content of the test material (i.e. 25.96%) the concentration of Vinasses in the aquatic samples was calculated and corrected for the control. No acute effects were observed based on growth rate and yield (EC50(72h) > 56 mg/L, measured, EC50(72 h): > 100 mg/L, nominal). Furthermore, under the conditions of the present study Vinasses did not induce growth rate reduction at a nominal concentration of 100 mg/l (NOEC), corresponding to an average exposure concentration of 56 mg/L. However, the test substance induced 23% inhibition of yield at a loading rate of 100 mg/L, i.e. the NOEC was below a loading rate of 100 mg/L corresponding to an average exposure concentration of 56 mg/L (for yield).
Similar to observations in the acute fish test on this substance, after two days of exposure onwards the limit concentration was observed to contain undissolved particles. There is no test on the water solubility of this test substance available, but for the similar UVCB substance, Vinasses, residue of fermentation containing biomass ofCorynebacterium glutamicum, it was shown that a large fraction of components with relatively high water solubility is existent (Oudhoff, 2010, OECD 105). However, the test substance was not completely soluble in water since in all samples undissolved test substance particles were observed. Nevertheless, large fractions exhibited a very high water solubility (38g/L at a loading rate of 100g/L, pH 3.5-3.6). Therefore, it can be concluded, that the observed hazyness and partly precipitations are rather a result of the variable composition of this test substance, than of a limited water solubility. It is likely that both bacterial activities together with the variable composition of the substance resulted in the observed precipitation.
Vinasses, residue of fermentation and vinasses, residue of fermentation, depotassified contain very similar dry matter contents and the same types of components with similar ranges.The test results obtained for Vinasses, residue of fermentation
on biodegradation, with fish (short term), daphnia (long term), algae and activated sludge reveal no persistency and no toxicity hazard for the aquatic environment. Therefore, based on the analogue justification approach,an analogy can be done on these properties between Vinasses, residue of fermentation and Vinasses residue of fermentation, depotassified.
Thus, Vinasses, residue of fermentation, depotassified, is considered to not induce growth rate reduction at a nominal concentration of 100 mg/L (NOEC), corresponding to an average exposure concentration of 56 mg/L.
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.