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Diss Factsheets
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EC number: 234-390-0 | CAS number: 11138-47-9
- 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
Hazard for air
Hazard for terrestrial organisms
Hazard for predators
Additional information
As a consequence of the decomposition behaviour of sodium perborate in aqueous solution and having in mind the analytical problems concerning the determination of perborates in water the results of laboratory tests on aquatic toxicity of sodium perborate do not allow conclusions on the nature of the substance or degradation products, to which the test species were exposed. The primary degradation product of sodium perborate in aqueous solution is boric acid. Furthermore exposure to hydrogen peroxide may occur as sodium perborate is in aqueous solutions in equilibrium with this substance (cf. 5.1.2). Concerning this exposure most aquatic organisms have developed detoxifying mechanisms to prevent cell damage. Antioxidant enzyme systems containing catalase decompose reactive oxygen species stepwise to water. More information on the ecotoxic effects of hydrogen peroxide can be found in the EU-Risk Assessment Report for this compound (ECB 2003). After degradation of hydrogen peroxide the remaining borate species should be the sole toxicologically relevant substances with sodium metaborate being the first degradation product. The most important borate species which will be present in aqueous media under environmental conditions should be boric acid (H3BO3). The ecotoxicity of boric acid has been reviewed in ECB (2009).
In ECB (2009), the PNEC for aquatic organisms for boron was derived based on added concentrations, in order to take both naturally and anthropogenic sources of boron into account. For practical reasons boric acid and other borates are usually expressed on the basis of boron. The PNECadd,aquatic for freshwater systems was set to 0.18 mg B/L. For microorganisms STPs, a PNECadd,STP of 1.8 mg B/L was calculated. The assessment for sediments was based on the equilibrium partitioning method, therefore no further risk assessment was performed. The PNECadd,terrestrial was set to 0.4 mg B/kg dwt soil, the value being based on toxicity tests on terrestrial organisms.
For hydrogen peroxide, the PNEC was calculated based on added concentrations i.e. background concentrations have been excluded (ECB 2003). The PNECaquatic was determined to be 10 μg/l and the PNECmicroorganisms to be 4.66 mg/l. For sediments and the terrestrial compartment, the PNECs were based on the equilibrium partitioning method, therefore no further risk assessment was performed.
Conclusion on classification
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.
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