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Diss Factsheets
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EC number: 215-157-2 | CAS number: 1308-06-1
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
In aquatic systems, cobalt accumulates from water to plants (BCF >100 to 5000), with higher trophic levels showing reduced accumulation; BCF ≤515 for invertebrates, with both freshwater and marine fish showing BCF/BAF < 10.
Of the 112 documents retrieved for cobalt aquatic bioaccumulation / bioconcentration, 54 were of relevant quality. The majority of the studies calculated BCF and/or BAF from the efflux kinetics through exposure either through water or diet as opposed to the ratio of the tissue to water or food burdens. BCFs for green algae, phytoplankton and higher plants (e. g., duckweed and fucus) varied greatly and were generally high, varying between 180 and 4000. However, this wide range of values is expected with essential metals, especially in situations where organisms are exposed to a range of environmental concentrations and physiological mechanisms are successfully functioning to maintain homeostatic concentrations. In those situations where external concentrations are low, active sequestration of cobalt is necessary to achieve adequate tissue concentrations. In these cases BCF values will be high while the opposite is true when concentrations are elevated. These organisms must actively sequester large concentrations of these materials in order to achieve physiologically necessary concentrations. Higher food chain organisms exhibited significantly reduced BCFs, ranging from 30-161 for bivalves (mussel and scallop), 265 and 515 for crustaceans D. magna and H. azteca, respectively, and <1 to 7 for freshwater (rainbow trout) and marine (sea bass) fish. A marine trophic transfer study (Mathews & Fisher, 2008) established cobalt tissue concentrations across a number of trophic pathways, incorporating phytoplankton, zooplankton, a sea break and sea bass. The reported trophic transfer value was <1. Though of limited quantity, these studies indicate that cobalt does not biomagnify through either freshwater or marine trophic foodwebs.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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