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EC number: 203-630-6 | CAS number: 108-93-0
- 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
Cyclohexanol exhibited effects to aquatic invertebrates (Daphnia magna) in standard aquatic toxicity studies conducted to GLP and OECD Testing Guidelines. The substance is classified for long-term aquatic hazard, Chronic Category 3, in accordance with the criteria for classification as defined in Annex I, Regulation (EC) No 1272/2008, as amended by Commission Regulation (EU) No 286/2011.
Additional information
Results on acute aquatic toxicity are available for the three trophic levels of fish, daphnia and algae. A chronic study on Daphnia magna is also available. The following endpoints have been selected for determining the hazard potential of cyclohexanol towards aquatic organisms on the basis of their reliability:
Fish
LC50 (96 hours) 704 mg/L, measured, Pimephales promelas, Brooke et al. 1984
Invertebrates
EC50 (48 hours) 17 mg/L, measured, Daphnia magna, SafePharm, 2003
NOEC (21 days) 0.953 mg/L, measured, Daphnia magna, Smithers Viscient, 2016
Algae
EC50 (72 hours) >500 mg/L, nominal, Scenedesmus subspicatus, BASF AG 1988
Cyclohexanol exhibited harmful effects to Daphnia magna, resulting in an EC50 (48 h) value of 17 mg/L (measured concentration) and a NOEC (21 d) value of 0.953 mg/L. This chronic NOEC represents the most sensitive endpoint for aquatic effects and is therefore used for the derivation of PNECs.
Results of toxicity tests towards aquatic microorganisms show that cyclohexanol is not harmful to bacteria. This was established in tests performed according to standard guidelines (BASF AG 1981, 1987).
EC20 (30 min) >1995 mg/L, nominal, industrial activated sludge, BASF AG 1981
EC10 (17 h) 470 mg/L, nominal, Pseudomonas putida, BASF AG 1987
Therefore, the inhibition of degradation activity of activated sludge is not anticipated when cyclohexanol is introduced in appropriately low concentrations.
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