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EC number: 237-714-9 | CAS number: 13939-25-8
- 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
Additional information
Aluminium dihydrogen triphosphate (CAS 13939-25-8) is poorly water soluble. The substance will be hydrolytically transformed into orthophosphate and aluminium ions in aqueous and biological systems. Aluminum is a naturally abundant element, the third most common element of the earth's crust. It is naturally released to the environment from the weathering of rocks and volcanic activity. Aluminum present in surface waters due to man-made applications cannot be distinguished from natural aluminum released during weathering of aluminum-bearing minerals. The emission of the registered substance is very low.
The phosphate anions are ubiquitous in natural waters and essential micronutrient for many organisms. In acidic aquatic systems, aluminium exists in natural waters as a number of species, including dissolved and particulate forms. This again depends on many factors, especially pH, alkalinity, temperature, dissolved organic carbon, dissolved inorganic carbon and anion concentration. Furthermore, hydrolysis of aluminium ions has two possible “directions” towards a neutral pH, i.e. base hydrolysis and acid hydrolysis. Both acid and base hydrolysis of aluminium rapidly results in precipitation of aluminium hydroxide, which can become adsorbed on suspended particles or immobilised in sediment. A direct release of aluminium dihydrogen triphosphate (CAS 13939-25-8) to terrestrial environment is negligible. If emitted to soil, depending on the buffer capacity of the soil, the substance will be neutralised and decomposes to aluminium hydroxide or oxide (gibbsite), that are stable and can become immobilised in soil. Nevertheless, as a result of this dynamic chemistry, the amount of aluminium associated with suspended particles is dependent on the chemical conditions. Factors that are known to affect aluminium speciation, such as pH and DOC, are also known to affect adsorption and desorption from particle surfaces. The adsorption potential of polyphosphates increases with increasing length of phosphate units i.e. the adsorption potential of triphosphate is higher compared to orthophosphate. Whereas the mobility and solubility in soil increases when the number of phosphate units is decreased, for example by hydrolysis of triphosphate to orthophosphate (Busman 1984).
The air compartment is considered not relevant for aluminium dihydrogen triphosphate (CAS 13939-25-8). Since these aluminum phosphates are usually not emitted to air, the amount of aluminum present in air that is related to the aluminum being considered here would be negligible compared with the amount coming from natural erosion of soil (Environment Canada Health Canada, 2008).
Reference
Busman, Lowell Marion, (1984)."Behavior of polyphosphates in soils " Retrospective Theses and Dissertations. Paper 8979.
Environment Canada Health Canada, (2008), Canadian Environmental Protection Act, 1999, PRIORITY SUBSTANCES LIST STATE OF THE SCIENCE REPORT; FOLLOW-UP TO THE STATE OF SCIENCE REPORT, 2000, Aluminum Chloride, Aluminum Nitrate, Aluminum Sulphate, November 2008
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