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EC number: - | CAS number: -
- 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

Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 6.87 µg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 30.1 µg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.687 µg/L
- Assessment factor:
- 100
- Extrapolation method:
- assessment factor
- PNEC marine water (intermittent releases):
- 3.01 µg/L
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 5.28 mg/L
- Assessment factor:
- 10
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- no hazard identified
Sediment (marine water)
- Hazard assessment conclusion:
- no hazard identified
Hazard for air
Air
- Hazard assessment conclusion:
- no hazard identified
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- no hazard identified
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
Conclusion on classification
Aluminium is the major constituent of "Neutralisation and reduction products of bauxite residue from refinement process" which is released in the transformation/dissolution (T/D) test (OECD Series on Testing and Assessment No 29, see IUCLID section 4.8) and is hence relevant for the environmental hazard and risk assessment. The Al compounds occurring in "Neutralisation and reduction products of bauxite residue from refinement process" (i.e. Al(OH)3 and Al(OH)O) are assumed to be the source of Al released in the transformation/dissolution test. Therefore, the classification of "Neutralisation and reduction products of bauxite residue from refinement process" is focused on Aluminium ions and evaluation strategy is based on read-across from existing Aluminium ecotoxicological studies.
As demonstrated in the T/D test, a loading rate of 100 mg substance/L at pH 8 results in a dissolved concentration of ca. 0.36 mg Al/L and 0.48 mg Al/L after 7 and 28 days, respectively.
Classification for acute aquatic hazards
The most sensitive species in acute aquatic tests is fish with a 96-h LC50 of 0.57 mg Al/L, corresponding to a 96-h LC50 of 3.01 mg "Neutralisation and reduction products of bauxite residue from refinement process"/L. As the most sensitive acute effect value is > 1 mg/L, a classification for acute aquatic hazards is not warranted.
Classification for chronic aquatic hazards
The most conservative chronic no-observed effect concentration (NOEC) of aluminium ions (Al3+) is 13 µg/L (0.013 mg/L) for fish reproduction. Back-calculated based on the estimated molecular weight range of "Neutralisation and reduction products of bauxite residue from refinement process" of ca. 142.48 – 254.91 g/mol, this results in a substance-based worst-case NOEC of 0.069 mg/L. Aluminium release from "Neutralisation and reduction products of bauxite residue from refinement process" may lead to dissolved Al3 + concentrations of up to 0.5 mg Al/L for 100 mg /L substance loading. Aluminium, as an element, cannot be further degraded hence needs to be considered as not rapidly degradable.
Based on the ECHA Guidance on the application of the CLP criteria (see https://echa.europa.eu/documents/10162/2324906/clp_en.pdf/58b5dc6d-ac2a-4910-9702-e9e1f5051cc5), Appendix IV, chapter IV.5.3.2.2, the poorly soluble substance "Neutralisation and reduction products of bauxite residue from refinement process" is classified into category Chronic 4, as the dissolved Al ion concentration obtained from the 7 day transformation test at the high loading rate (100 mg/l) of 0.36 mg/L is lower than the acute ERV of 0.57 mg AL/L and there is no evidence of rapid environmental transformation and no bioaccumulation.
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