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EC number: 236-921-1 | CAS number: 13548-38-4
- 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
Description of key information
Additional information
A 20-week study was conducted early in 1968 with chromium trinitrate to corroborate an earlier experiment on uptake by Crassostrea virginica. About 200 November-harvested oysters were placed in each of eight 120-liter tanks making use of a flow-through sewer water system. During the acclimatisation and experimental periods the sea water was maintained at a flow rate of 2.5 l/min and a 20 ±1 degree C temperature with salinity variable but usually 31 ± 2 ppt. The test animals were subjected to continuous levels of the test substance at 0.05 ppm and 0.1 ppm. Each week the test animals were removed for analysis.
The test result indicated the metal in the tissues of the test animals ranged from less than 0.21 ppm to 6.28 ppm at 0.05 ppm concentration group and ranged from less than 0.21 ppm to 11.49 ppm at 0.1 ppm concentration group.
The BCF for the test substance was not specified in this study. However, it was indicated to be 116 as reported in the AMBIENT WATER QUALITY CRITERIA FOR CHROMIUM published by U.S. ENVIRONMENTAL PROTECTION AGENCY.
Accumulation and elimination of chromium of the earthworm Eisenia andrei was determined in an artificial soil through exposure to chromium trinitrate. Five concentration groups of 10, 32, 100, 320 and 1000 mg/kg dw soil and control group were administrated to the test earth worms. Chromium was significantly accumulated and earthworm reproduction significantly reduced at soil concentrations of 100 mg/kg and higher. Chromium was completely eliminated and reproduction no longer affected at the end of a 3-week recovery period. BCF values for the accumulation of chromium in the worms were 0.031-0.047 at the three lowest and 0.016-0.019 at the two highest dose levels. Control soil contained 6.3 mg Cr/kg dry weight; the BCF value for worms kept in this soil therefore is 0.048.
In summary it can be stated that chromium (III) does not significantly bioaccumulate in American oysters and does not bioaccumulate in earthworms.
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