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EC number: 232-140-5 | CAS number: 7789-00-6
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
Description of key information
The substance forms reversible equilibria and the proportion of the species present depends on various environmental factors. An overview of the expected behaviour of the substance in sterile aqueous media is provided in the EU RAR, furthermore the speciation of the substance is affected by various other reducing or oxidising species present:
Key value for chemical safety assessment
Additional information
There are no proprietary studies investigating the hydrolysis of the substance in aqueous media. The substance of interest is an inorganic element and sufficient information on the speciation of the substance under various environmental conditions is available in the EU RAR for chromium (VI) compounds (2005): further details are provided below.
Ionic equilibria for chromium (VI)
Chromium (VI) is a strong oxidising agent and as a result only exists as oxygenated species in the environment. For the dichromates, the actual species present in solution depends on the pH according to the following equilibria:
H2CrO4¿ H+ + HCrO4- pKa1 = -0.6; 0.74; 0.86
HCrO4-¿ H+ + CrO42- pKa2 = 5.9; 6.49; 6.51
Based on these equilibria alone, at very low pH (e.g. near 0) the dominant species in solution would be the fully protonated form (H2CrO4). At pHs between 0 around 6-6.5, the dominant chromate species in solution would be HCrO4-, and at pHs above around 6-6.5 the main chromate species in solution would be CrO42-.
In addition to the above equilibria, the chromate ion is in equilibrium with the dichromate ion according to the following equilibria:
2CrO42-+ 2H+ ¿ Cr2O72- + H2O
2HCrO4-¿ Cr2O72- + H2O
In addition, there are the following base-hydrolysis equilibria:
Cr2O72-+ OH- ¿ HCrO4- + CrO42-
HCrO4-+ OH- ¿ CrO42- + H2O
Overall, the available information indicates that at very low pH values (1) the main species in solution is H2CrO4, at higher pHs between around 2 and 6, HCrO4- and Cr2O72-will both be present in equilibrium, and at higher pHs (>7) the main species present will be CrO42-. Thus at environmental pHs the species found in solution will be a mixture of Cr2O72-, HCrO4- and CrO42-, irrespective of the form in which the chromium (VI) enters solution.
Ionic equilibria for chromium (III)
The predominant forms of chromium (III) present in solution are Cr3+ at very low pH, then with increasing pH, Cr(OH)2+, Cr(OH)2+, Cr(OH)3 and finally Cr(OH)4- at very high pH. The species Cr(OH)2+ is thought to occur only over a very narrow pH range (approximately pH 6.27-6.84).
In solution, the equilibrium between chromium (III) ions and chromium hydroxide lays well over to the side of the relatively insoluble hydroxide at pH>5 according to the following equilibrium:
Cr3++ 3H2O ¿ Cr(OH)3 (s) + 3H+ Keq = 1.10-12
This means that at pHs >5 chromium (III) can be expected to precipitate out of solution as the insoluble hydroxide, often in conjunction with iron. However, complexation of chromium (III) ions with organic matter (such as citric acid, diethylenetriaminepentaacetic acid (DTPA), fulvic acid) can result in increased solubilisation of chromium (III) at higher pHs.
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