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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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The 72h ErL50 for Lime Oxide was 15mg/L based on loading rates. These value can be used directly for classification but is unsuitable for derivation of PNEC since partitioning in the environment of the two groups of components present in Lime oxide will make comparison with PEC meaningless. In order to derive appropriate PNECs, acute daphnia information for the two assessment entities has been used since the daphnia endpoint was identified as the most sensitive species for both groups (see aquatic toxicity endpoint summary for details).
For the purposes of classification and labelling, data on the whole substance is used. A study performed on Lime oxide gave an ErL50 of 15mg/L and an ErL10 of 11mg/L based on WAF loading rates.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 15 mg/L
- EC10 or NOEC for freshwater algae:
- 11 mg/L
Additional information
A study was performed to assess the effect of the registered substance on the growth of the green alga, Pseudokirchneriella subcapitata. Since the substance is a complex mixture composed of components with different water solubility (i.e. unsaturated monoterpene hydrocarbons and oxygen-containing monoterpenes), the test item was prepared as Water Accomodated Fractions (WAFs). As components of the test item were suspected to be volatile, the test was conducted in completely filled, stoppered vessels to minimise possible losses due to volatilization. Following a preliminary range-finding test, Pseudokirchneriella subcapitata was exposed to Water Accommodated Fractions (WAFs) of the test item over a range of nominal loading rates of 10, 18, 32, 56 and 100 mg/L (three replicate flasks per concentration) for 72 hours. GC analysis using the total peak area associated with the test item, showed measured test concentrations at 0h of 0.918, 1.81, 4.2, 10.1 and 22.5 mg/L. Measured test concentrations after 72 hours were 84 to 96% of initial, indicating that the dissolved test item concentration had been maintained throughout the exposure period.
Given that the toxicity cannot be attributed to a single component or a mixture of components but to the test item as a whole, the results were based on nominal loading rates only. The 72h ErL50 and ErL10 were determined to be 15 and 11mg/L respectively. Both values have been considered in the environmental classification of the registered substance.
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