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EC number: 215-269-1 | CAS number: 1317-38-0
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
High quality single-species EC50 values and NOEC/(L(E) C10 values are available for 3 freshwater algae species. A chronic Biotic Ligand Model was developed for S. Subcapitata and validated for 3 additional speicies. The NOECs and the chronic algae Biotic ligand models (BLM) are carried forward to the risk characterisation.
High quality chronic single-species NOEC/(L(E) C10 values are available for 4marine algae species. The observed effects are related to the organic carbon content of the test waters. The NOECS and organic carbon relationships are carried forward to the risk characterisation.
Key value for chemical safety assessment
Additional information
Freshwater algae NOECS
High quality chronic NOEC/(L(E) C10 values are available for 3 species:Chlamydomonas reinhardti, Chlorella vulgaris and Pseudokirchernella subcapitata.
The NOECs were used to calculate high quality “species geometric mean” NOEC values for each endpoint and the most sensitive endpoint for each of the algae species was retained as "species-mean" NOEC. The "species mean" NOEC value range from 43 µg/l Cu forPseudokirchernella subcapitata(endpoint growth; n=4) to 138 µg/l Cu forChlorella vulgaris(endpoint growth; n=17). These values are used for the PNEC derivation.
Large intra-species variability are observed. The effects data-set fromPseudokirchernella subcapitatawas used for the development of an algae BLM (De Schamphelaere et al, 2003) The capacity of the BLM for predicting copper toxicity to other algae species was demonstrated from copper toxicity studies withChlamydomonas reinhardtiandChlorella vulgaris(De schamplelaere and Janssen, 2006).
Research related to copper acclimation and deficiency (Bossuyt et al, 2004) demonstrated that, based on the algal biomass, the growth rate, the pigment diversity and the autotrophic index, an optimal concentration range was observed between 1 and 35µg Cu/L. Deficiency was observed at lower levels, toxicity was observed at higher levels.
Marine algae NOECS
High quality chronic NOEC values are available for 4 species: 2 diatoms (Phaeodactylum tricornutumandSkeletonema costatum) and 2 macroalgae (Macrocystis pyriferaandFucus vesiculosis). Individual NOEC values range between 2.9 µg Cu/L (Phaeodactylum tricornutum, growth) to 50 µg Cu/L(MacrocystisPyrifera, germination).
High quality “species mean” NOEC values are derived for the most sensitive endpoint for each of the 4 species of marine algae. The"species mean" NOEC value range from 2.9 µg/l Cu for thePhaeodactylum tricornutumto 11 µg/l forFucus vesiculosis. Large intra-species variability are observed due differences inDOC. A relation between the observed NOEC and organic carbon content was established forFucus vesuculosis.
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