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EC number: 277-225-8 | CAS number: 73018-51-6 The complex combination of hydrocarbons obtained by the acid isomerization of linalool. It consists primarily of monoterpenes, terpene alcohols and oxygenated cyclic compounds.
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
For the purposes of the environmental risk assessment, two assessment entities have been defined. For both groups, the daphnia endpoint was identified as the most sensitive species (see aquatic toxicity endpoint summary for details). The following 48h EC50 values have been estimated and used to derive PNECaquatic for the corresponding assessment entities:
- Unsaturated Monoterpene Hydrocarbons: 0.215 mg/L (lowest QSAR value of all component predictions)
- Monoterpene Ethers: 32mg/L (based on the representative substance, Limetol)
For the purposes of classification and labelling, data on the whole substance is used. A study performed on Lime oxide gave an acute 48h EL50 of 5.3mg/L based on WAF loading rates.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 5.3 mg/L
Additional information
A study was performed to assess the acute toxicity of the registered substance to Daphnia Magna. The test item is a complex mixture composed of constituents with different water solubility (i.e. unsaturated monoterpene hydrocarbons and oxygen-containing monoterpenes) and therefore the test item was prepared as Water Accommodated Fractions (WAFs). Following a preliminary range-finding test, twenty daphnids (4 replicates of 5 animals) were exposed to Water Accommodated Fractions (WAFs) of the test item over a range of nominal loading rates of 2.6, 6.2, 16, 40 and 100 mg/L for 48 hours at a temperature of approximately 20 °C under static test conditions. The number of immobilized Daphnia and any adverse reactions to exposure were recorded after 24 and 48 hours. The test item was suspected to be volatile and hence testing was conducted in completely filled, stoppered test vessels in order to minimize possible losses due to volatilization.
GC analysis using the total peak area associated with the test item, showed measured test concentrations at 0h of 0.892, 1.76, 4.25, 10.2 and 21.8mg/L. Measured test concentrations after 48 hours were 84 to 100% of initial, indicating that the dissolved test item concentration had been maintained throughout the exposure period.
The dissolved test item may have been one or several components of the test item. Given that toxicity cannot be attributed to a single component or mixture of components but to the test item as a whole, the results were based on nominal loading rates only. The determined 48h EL50 was 5.3 mg/L. This value has been used for classification of the registered substance.
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