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Diss Factsheets
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EC number: 906-627-4 | 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
The NOEC for the reaction mass was derived from the most sensitive value for one single component of the mixture. In order to this, the NOEC for the reaction mass is > 0.953 mg/l.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- NOEC
- Effect concentration:
- 0.953 mg/L
Additional information
To assess the chronic toxicity of cyclohexanol to aquatic invertebrates a GLP study according to OECD guideline 211 was conducted with daphnia magna. The test organisms were exposed to the nominal concentrations: 0, 0.1, 0.32, 1.0, 3.2 and 10 mg/L for 21 d in a semi static system. The time weighted mean measured concentrations were 0.0445, 0.0962, 0.224, 0.953 and 4.09 mg/L, equivalent to 45, 30, 22, 30 and 41% of nominal concentrations, respectively. Under the conditions of this study, the NOEC value for adult survival was considered to be 0.953 mg/L. The EC50 for adult survival was considered to be 1.775 mg/L. The NOEC value for juvenile production was considered to be 0.953 mg/L and the EC50 for juvenile production was considered to be greater than 0.953 mg/L. The NOEC value for growth was considered to be 0.953 mg/L and the EC50 for growth was considered to be greater than 0.953 mg/L. All values were based on time weighted mean measured concentrations.
No experimental studies are available to assess the long-term toxicity to aquatic invertebrates of cyclohexanone. Therefore, the toxicity was predicted by the scientifically valid QSAR software QSAR Toolbox v4.3.1; Database v4.3.1. The substance is within the applicability domain of the model. The predicted NOEC after 21 d was 26.6 mg/l.
The NOEC for cyclohexanol is more sensitive (0.953 mg/l) than the with QSAR predicted NOEC for cyclohexanone (26.6 mg/l) and it resulted from an experimental study. Therefore, the NOEC for the reaction mass can be derived from the NOEC of the single component. By choosing the most sensitive value of one component the worst-case scenario for the mixture is covered. In order to this, the NOEC for the reaction mass is 0.953 mg/l.
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