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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
Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
There are no toxicokinetic studies available for Tricobalt dicitrate. However, there are reliable data available for structurally related cobalt compounds.
Absorption
Inhalation: Inhalation of cobalt particles results in deposition in the upper and lower respiratory tract (Casarett and Doull, 1986). Particle size is the primary factor determining deposition patterns. Large particles (diameter > 2 µm) deposit in the upper respiratory tract, while smaller particles tend to deposit in the lower respiratory tract, where sedimentation and diffusion can occur. Fractional deposition varies due to particle size, age and breathing patterns of the exposed individuals. Cobalt particles deposited in the respiratory tract can be absorbed into the blood after dissolution or mechanically transferred to the gastrointestinal tract by mucociliary action and swallowing (Foster et al., 1989).
Oral: The absorption of cobalt salts after oral administration is dependent on their water solubility. Water soluble cobalt salts dissolve directly and have been found to exhibit greater absorption than non-water soluble compounds (Firriolo et al., 1999).
Studies of the absorption of cobalt(II)chloride in human volunteers indicate that the absorption rate from the gastrointestinal tract ranges from 5% to > 20%, depending on the dose and the nutritional status of the individual (Smith et al., 1972; Sorbie et al., 1971). Cobalt absorption was increased among individuals (humans and animals) who were iron deficient (31-71% absorption in iron-deficient subjects, 18-44% in controls) (Valberg et al., 1969; Sorbie et al., 1971). The gastrointestinal absorption is reduced when cobalt is administered after a meal (Midtgard and Binderup, 1994).
Dermal: The available data indicate that the in vivo dermal absorption rate in guinea pigs was in the same range as the in vitro dermal absorption rate reported for humans (51-86 and 38 nmol/cm2/h, respectively; application of 0.085 M cobalt(II)chloride) (Wahlberg, 1965). Dermal exposure to cobalt(II)chloride may result in significant systemic uptake of cobalt.
Distribution and excretion
After inhalation exposure in animals, marked increases of cobalt have been found in the lung. Histological analysis revealed that cobalt particles were localised to macrophages within the bronchial wall or in the interstitium close to the terminal bronchiole. Cobalt has been found also in the liver, kidney, trachea, spleen, bones and heart with the highest level in the liver and kidney (Brune et al., 1980).
The distribution of cobalt after oral administration in rats indicated that cobalt absorbed in the gastrointestinal tract is primarily retained in the liver. But cobalt was also found in the kidneys, heart, stomach, and intestines (Ayala-Fierro et al., 1999).
Animal data on cobalt elimination indicate that the solubility of the cobalt compound greatly affects the long-term clearance. Soluble cobalt compounds are absorbed into the blood at a faster rate than less soluble compounds and excreted in the urine and faeces (Barnes et al., 1976). Urinary excretion rates seem to correlate with the translocation rate of cobalt from the lungs to blood, whereas faecal excretion rates seem to correlate with mechanical clearance rates of cobalt from the lungs to the gastrointestinal tract (Collier et al., 1989; Patrick et al., 1989). Following an initial high rate of faecal clearance, urinary excretion is the primary route of cobalt elimination after inhalation exposure (Palmes et al., 1959).
After oral administration, faecal elimination is the primary route of excretion. Ayala-Fierro et al. (1999) showed that cobalt(II)chloride was excreted primarily via faeces in rats (70-83% of the administered dose), with urinary excretion for the remainder of the dose. Faecal clearance has been noted to decrease as cobalt particle solubility increases.
Following single intravenous administration of cobalt(II)chloride to rats, 10% of the dose was excreted in faeces indicating biliary excretion and 75% of the dose was excreted in urine 36 hours after administration (Ayala-Fierro et al., 1999).
References:
Casarett LJ and Doull J, 1986, The basic science of poisons, 3rd ed. New York , Macmillan Publishing Company, pp. 56-57
Foster PP et al., 1989, An interspecies comparison of the lung clearance of inhaled monodisperse cobalt oxide particles – Part II: Lung clearance of inhaled cobalt oxide in man. Journal of Aerosol Science, 20(2): 189-204
Firriolo JM et al., 1999, Absorption and disposition of cobalt naphthenate in rats after a single oral dose. Journal of Toxicology and Environmental Health A, 58: 383-395
Smith T et al., 1972, Absorption and retention of cobalt in man by whole-body counting. Health Physics, 22: 359-367
Sorbie J et al., 1971, Cobalt excretion test for the assessment of body iron stores. Canadian Medical Association Journal, 104(9): 777-782
Valberg LS et al., 1969, Alteration in cobalt absorption in patients with disorders of iron metabolism. Gastroenterology, 56(2): 241-251
Midtgard U and Binderup ML, 1994, The nordic expert group for criteria documentation of health risks from chemicals. 114. Cobalt and cobalt compounds. Arbete och Hälsa, 39: 1-66
Wahlberg J., 1965, Percutaneous absorption of sodium chromate (51Cr), cobaltous (56Co), and mercuric (203Hg) chlorides through excised human and guinea pig skin. Acta Derm Venerol, 45: 415-426
Brune D et al., 1980, Pulmonary deposition following inhalation of chromium-cobalt grinding dust in rats and distribution in other tissues. Scandinavian Journal of Dental Research, 88: 543 -551
Ayala-Fierro F et al., 1999, Disposition, toxicity and intestinal absorption of chloride in male Fischer 344 rats. Journal of Toxicology and Environmental Health A, 56: 571-591
Barnes JE et al., 1976, Cobalt-60 oxide aerosols: Methods of production and short-term retention and distribution kinetics in the beagle dog. Health Physics, 30: 391-398
Collier CG et al., 1989, An interspecies comparison of the lung clearance of inhaled monodisperse cobalt oxide particles – Part V: Lung clearance of inhaled cobalt oxide particles in hamsters, rats and guinea pigs. Journal of Aerosol Science, 20(2): 233-247
Patrick G et al., 1989, An interspecies comparison of the lung clearance of inhaled monodisperse cobalt oxide particles – Part V: Lung clearance of inhaled cobalt oxide particles in SPF Fischer rats. Journal of Aerosol Science, 20(2): 249-255
Palmes ED et al., 1959, Inhalation toxicity of cobalt hydrocarbonyl. American Industrial Hygiene Association Journal, 20: 453-468
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