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EC number: 244-168-5 | CAS number: 21041-95-2
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
Freshwater: chronic sediment data are available for one species of benthic nematode
(Caenorhabditis elegans) with a reported NOEC growth of 1225 mg/kg d.w. (geometric mean of three NOECs from same study). The test was performed in unpolluted sediment with a background cadmium concentration of <1 mg/kg d.w. In addition, an in-situ recolonization study is also available for freshwater systems with a NOEC abundance reported of 115 mg/kg d.w. The test was performed in unpolluted sediment with a background cadmium concentration of 2.8 mg/kg d.w.
Marine water: chronic sediment data are available for one species of benthic marine crustacean (Leptocheirus plumulosus) with a reported NOEC growth, survival and reproduction of 1370 mg/kg d.w. The test was performed in unpolluted sediment with a background cadmium concentration of <0.001 mg/kg d.w. In addition, a field colonization study is also available for marine systems with a reported NOEC abundance and taxa richeness of 169 mg added Cd/kg d.w.
Key value for chemical safety assessment
Additional information
Freshwater PNECsediment: Conclusion
The assessment of the freshwater PNECsedimentfor cadmium identified only two long-term ecotoxicity studies from the scientific literature. However, both the “Added” EqP (using partitioning coefficients and a robust aquatic toxicity database from the Cd RAR) and AF (using the lowest NOEC from a field colonization study) approaches produced consistent derivations for the freshwater benthic compartment. The resulting value is considered protective for EU freshwater ecosystems: freshwaterPNECadd, sediment of 1.80 mg/kg d.w. (equivalent to 0.40 mg/kg w.w.). It is emphasized that this is an added PNEC, i.e. natural background needs to be taken into account when characterising the risk from monitored data.
Marine PNECsediment: Conclusion
The assessment of the marinePNECsedimentfor cadmium identified only two long-term ecotoxicity studies from the scientific literature. However, an “Added” EqP (using partitioning coefficients and a robust aquatic toxicity database) approach provided a reliable derivation for the marine benthic compartment. The resulting value is considered protective for EU marine ecosystems:marinePNECsediment, addedof 0.64 mg/kg d.w. (equivalent to 0.14 mg/kg w.w.). It is emphasised that this is an added PNEC, i.e. natural Bg needs to be taken into account when characterising the risk from monitored data.
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