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EC number: 244-492-7 | CAS number: 21645-51-2
- 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
The available evidence shows the absence of aluminium biomagnification across trophic levels both in aquatic and terrestrial food chains. The existing information suggests not only that aluminium does not biomagnify, but rather that it tends to exhibit biodilution at higher trophic levels in the food chain. More detailed information can be found in the attached document (White paper on waiving for secondary poisoning for Al & Fe compounds final report 02-02-2010. pdf).
Key value for chemical safety assessment
Additional information
Bioconcentration factors (BCF) and/or bioaccumulation factors (BAF) are typically calculated in order to estimate bioaccumulation and biomagnification. However, it has recently been demonstrated that unlike many organic substances, the BCF/BAF is not independent of exposure concentration for many metals (Brix and Deforest, 2000 and Mc Geer et al., 2003). Rather it is inversely related (i. e., decreasing BCF/BAFs with increasing exposure concentration) to exposure concentration. Metal concentrations in tissue based on a range of exposure concentrations may be quite similar but the BCFs will be quite variable reflecting an inverse relationship (i. e., higher BCFs at lower exposure concentrations and lower BCFs at higher exposure concentrations) between metal concentrations and the corresponding BCF (Brix et al, 2001). From the above it is clear that any conclusion based on the application of classical concepts (e. g., use of bioconcentration factors; BCF -biomagnification factors; BMF) to metals as they are applied to organic substances should be treated with caution. As a result, use of a simple ratio Cbiota/Cwateror Cbiota/Csediments as an overall approach for estimating bioconcentration factors for aluminium body burdens is not appropriate.
References:
Brix KV, DK DeForest. 2000. Critical review of the use of bioconcentration factors for hazard classification of metals and metal compounds. OECD (Organization for Economic Cooperation and Development) Aquatic Hazards Extended Workshop Meeting, May 15, Paris, France.
Brix, K. V., DeForest, D. K. and Adams, W. J. (2001), Assessing acute and chronic copper risks to freshwater aquatic life using species sensitivity distributions for different taxonomic groups. Environmental Toxicology and Chemistry, 20: 1846–1856.
Herrmann and Frick. 1995. Do Stream Invertebrates Aluminium at low pH conditions?Water, Air and Soil Pollution 85: 407-412.
McGeer et al. 2003. Inverse relationship between bioconcentration factor and exposure concentration for metals; implications for hazard assessment of metals in the aquatic environment. Env. Tox. And Chem. Vol 22, No 5.
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