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Diss Factsheets
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EC number: 212-751-3 | CAS number: 866-81-9
- 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
Information taken from CICAD (2006):
60Co is taken up by unicellular algae with reported concentration factors (dry weight) of 40 000 for Scenedesmus obliquus and 18 000 for Selenastrum capricornutum (Nucho et al., 1988; Corisco & Carreiro, 1999). Freshwater molluscs have concentration factors of 100–14 000 (~1–300 in soft tissue). Much of the cobalt taken up by molluscs and crustaceans from water or sediment is adsorbed to the shell or exoskeleton; very little cobalt is generally accumulated in the edible parts (Amiard & Amiard-Triquet, 1979; Smith & Carson, 1981). Similarly, in laboratory studies with Daphnia magna, adsorption to the exoskeleton was the major contamination process (Adam et al., 2001). In studies with starfish (Asterias rubens), accumulation of 57Co was found to be predominately from seawater rather than from food (Warnau et al., 1999). Bioaccumulation factors for marine fish and freshwater fish are 100–4000 and <10–1000, respectively (Smith & Carson, 1981). However, accumulation is mostly in the viscera and skin of the fish, not the edible parts of the fish (Smith & Carson, 1981). In carp (Cyprinus carpio), accumulation from water accounted for 75% of 60Co accumulated from both water and food; accumulation from water and food was additive (Baudin & Fritsch, 1989). Depuration halflives were 53 and 87 days for fish contaminated from food and water, respectively (Bandin & Fritsch, 1989). Biomagnification of cobalt up the food-chain does not occur (Smith & Carson, 1981).
The study by Baudin and Fritsch (1989) compared radio-labelled cobalt uptake (Co60) from feed, from water and from a combination of both sources. The average retention factor after 63 days was in the order of 3 to 3.5 * 10E-3. The depuration period (70 to 80%) was between 63 and 49 days for sole aqueous and for sole feed contamination, respectively. In the event of accidental pollution of a waterway by this radionuclide, the radioactivity measured in the fish after passage of the contaminated water can be considered as a maximum value.
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