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EC number: 273-708-2 | CAS number: 69011-71-8 A scum formed on the surface of molten aluminum and molten aluminum alloys.
- 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
Aluminium dross is not expected to be absorbed via the gastrointestinal tract after oral administration. This is inferred by the study of acute toxicity via oral route (conducted as limit test) where no sign of systemic toxicity was found. Acute toxicity via inhalation route was not feasible since it was not possible to generate an appropriate inhalation atmosphere. Read-across to aluminium metal revealed an acute inhalation LC50 of more than 1000 mg/m3. No other constituents of Al dross present a significant toxicological profile on acute inhalation. Studies on dermal exposure were disregarded since dermal contact in the production and/or use is unlikely and inhalation is likely
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- LC50
- Value:
- 11 180 000 mg/m³
Acute toxicity: via dermal route
Endpoint conclusion
- Value:
- mg/kg bw
Additional information
Aluminium dross is not expected to be absorbed via the gastrointestinal tract after oral administration. This is inferred by the study of acute toxicity via oral route (conducted as limit test) where no sign of systemic toxicity was found.
Acute toxicity via inhalation route was not feasible since it was not possible to generate an appropriate inhalation atmosphere. Read-across to aluminium metal revealed an acute inhalation LC50 of more than 1000 mg/m3. No other constituents of Al dross present a significant toxicological profile on acute inhalation.Studies on dermal exposure were disregarded since dermal contact in the production and/or use is unlikely and inhalation is likely.
A study on acute toxicity of aluminium metal inhalation which may be used for derivation of LC50inhfor aluminium dross shows that aluminium metal powder is not acutely toxic. Furthermore, aluminium (CAS: 91728-14-2) has been characterized as a non-hazardous nuisance dust; the higher the concentration of dust the greater the risk of irritation to the respiratory system and mechanical irritation to the eyes. As a result aluminium should be addressed as a benign dust (poorly soluble dust with low toxicity).
No studies on acute toxicity of aluminium oxide inhalation are available in literature. Chronic toxicity studies show that inhalation of up to 75 mg/m3 for 6 months did not produce adverse local or systemic effects (see also 5.6.1.2). Further studies showed that aluminium oxide fibres of inhalable size did not produce fibrosis or malignancies after 2 year inhalation (see also 5.6.1.2). Finally, aluminium oxide (CAS: 1344 -28 -1) has been characterized as a non-hazardous nuisance dust; the higher the concentration of dust the greater the risk of irritation to the respiratory system and mechanical irritation to the eyes . As a result aluminium oxide should be addressed as a benign dust (poorly soluble dust with low toxicity).
No studies on acute toxicity of aluminium nitride inhalation are available in literature. This substance however disintegrates into aluminium hydroxide and ammonia upon contact with water and bodily fluids as will happen within the respiratory tract.Aluminium hydroxide (alumina hydrate) (CAS:21645 -51 -2)is an inert dust which is extensively used in pharmaceuticals, personal care products and foodstuffs, thus its safety has been verified. Aluminium hydroxide is purchased as an antacid drug or against hyperphosphataemia under a variety of brand names in Europe and US (Alamag®, Maalox®, Mylanta® Alternagel®, Alu-Cap®, Dialume®, Amphojel®, Alu-Tab®, Aloh-Gel® etc). Aluminium hydroxide is also used as an adjuvant to the diphtheria and pertussis toxoid for infant immunization. In, aluminium hydroxide is an approved colour additive (CI 77002) that may be used in all types of cosmetics and personal care products (Annex IV of Cosmetics Directive 76/768/EEC). FDA also permits aluminium hydroxide to be used as anindirect food additive. The wide use of aluminium hydroxide even in injecting preparations verifies its high safety profile. Furthermore, aluminium hydroxide has been characterized as a non-hazardous nuisance dust; the higher the concentration of dust the greater the risk of irritation to the respiratory system and mechanical irritation to the eyes . As a result aluminium hydroxide should be addressed as a benign dust (poorly soluble dust with low toxicity).
Ammonia is an upper respiratory irritant which has been
extensively studied due to its frequent production during a variety of
industrial and biological activities.
An acute toxicity study on ammonia inhalation is available which may be
used for derivation of LC50 inhalation for aluminium dross.
If all AlN (15% w/w of Al dross) is stoichiometrically transformed to ammonia an amount of 1677 mg AlN (11.18 g Al dross/L) would be needed for exertion of the aforementioned toxicological effect. It can therefore be claimed that the produced ammonia does not contribute to the toxicological effects of acute inhalation of Al dross.
Concerning the constituents of Aluminum dross the median lethal concentrations causing 50% lethality are:
LC50 (Aluminium dross): study technically non-feasible
LC50 (Aluminium metal): LC50>1 mg/L,non-hazardous nuisance dust
LC50 (Aluminium oxide) : -, non-hazardous nuisance dust
LC50 (Aluminium hydroxide) :-, non-hazardous nuisance dust
LC50 (ammonia)> 11.18 g /L (extrapolated to Al dros
The overall results of the OECD Guideline 403 (Acute Inhalation Toxicity test substance preparation indicate that the physical properties of the test substance prevented the achievement of the required consistency for proper aerosolization. Therefore, the EPA guidelines for acute inhalation testing could not be satisfied and a waiver from this testing should be granted.
Justification for classification or non-classification
No LD50 could be determined at the Acute Oral Toxicity test. No mortalities or other adverse effects were observed at the highest dose of 2000mg/kg of body weight. Therefore, LDoral50>2000mg/kg bw.
The inhalation study was not technically feasible, since it was not possible to generate an appropriate inhalation atmosphere in the laboratory.
Dermal exposure is not considered relevant due to absence of absorption through the skin for all constituents of the substance.
The impurities of aluminium dross are either of insignificant toxicological profile or of concentrations insufficient to trigger relevant classification for the whole mixture
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