Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 233-135-0 | CAS number: 10043-01-3
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The pH significantly alters the speciation and therefore bioavailability of the aluminium such that acutely toxic concentrations occur below a pH of 6 but that above 6 the bioavailable concentration necessary to achieve mortality to fish in an acute study cannot be achieved.
Key value for chemical safety assessment
Additional information
Five valid studies on fish were available on two aluminium salts:
Aluminum sulphate
Two short-term studies with fish are available on the 14-hydrated salt. Both tests were performed with Danio rerio. One test was a static study without pH adjustment. In this test an LC50 was found of 1 mg/l (dissolved Al) equivalent to 9.4 mg/L total aluminium at a pH of approximately 5.
The second test was performed under semi-static conditions with pH adjustment. The test substance concentrations were in a range of 62.5 to 1000 mg/l (nominal), eqivalent to 4.87 to 85.9 mg/L Total aluminium (measured) resulting in dissolved aluminum concentrations of 0.247 to 0.105 mg/l (the dissolved Al concentration decreased with increasing nominal concentrations). The pH was maintained at approximately 7.5. No effects were found in this test, therefore, LC50 is greater than 0.247 mg/l (dissolved Al) equivalent to 85.9 mg/L total aluminium , which was the maximum soluble concentration under the test conditons.
One supporting study from Kimball (1978) is available on the aluminium sulphate 16-hydrated salt. The nominal concentrations found that led to the 96 h LC50 are in line with those from the other studies.
Aluminum chloride, basic
Two short-term studies with fish are available. Both tests were performed with Danio rerio. One test was static without pH adjustment. In this test at a pH between 4.7 and 8.3 an LC50 was found of 186 mg/L nominal corresponding to 1.39 mg/l (dissolved Al) or 16.9 mg/L Total aluminium (measured). However, there was a strong division in pH across the test with nominal concentrations of 250 mg/L or higher at pH <5 and nominals at 125 mg/L or below at pH greater than or equal to 6.9. All fish at pH <5 died within 24 h of exposure while all fish at pH6.9 or above survived throughout the study.
The second test was semi-static with pH adjustment. The test substance concentrations were in a range of 62.5 to 1000 mg/l (nominal), this resulted in dissolved aluminum concentrations of 0.082 to 0.156 mg/l and 5.25 to 87.5 mg/L Total aluminium (measured). The pH was between 7.5 and 8.2 and 7.5 to 7.9 at the highest concentration at which no effects were found, therefore, LC50 is greater than 0.156 mg/l (dissolved Al) and 87.5 mg/L Total aluminium (measured).
Conclusion
Of the four available valid studies, two find no effects at the end of the study with Total aluminium concentrations of at least 85.9 mg/L (up to 87.5) and dissolved concentrations measured at a minimum of 0.156 mg/L (up to 0.247 mg/L) elemental Al. These studies were performed under standard Guidleine conditions at a pH between 7.5 and 8. In the two remaining studies, effects were found with Total alumuinium concentrations between 9.4 and 16.9 mg/L and dissolved aluminium concentrations ranging from 1 to 1.39 mg/L. In these cases the pH was not corrected to Guideline recommended values in the study and significant reduction of pH below 6 (at approximately 5) occurrred in solutions where immobilisation was observed.Thus it can be concluded that the pH significantly alters the speciation and therefore bioavailability of the aluminium such that acutely toxic concentrations occur below a pH of 6 but that above 6 the bioavailable concentration necessary to achieve mortality to fish in an acute study cannot be achieved.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.