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Diss Factsheets
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EC number: 231-765-0 | CAS number: 7722-84-1
- 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
The EU risk assessment report for hydrogen peroxide (European Commission 2003) comes to the following conclusion with regard to biodegradation of the substance (pp. 33/34): “On the basis of the available biodegradation tests it is possible to conclude that the substance is biodegraded under environmental conditions. The observed biodegradation rates of hydrogen peroxide are high and half-lives are short enough to fulfil the criterion “readily biodegradable” (10-day window criterion fulfilled) concerning the degradation rate. Hydrogen peroxide can therefore be considered as readily biodegradable in the aquatic compartment including sewage treatment plant. The simulation test results show that in most cases biodegradation seems to be the dominant and rate determining degradation pathway of hydrogen peroxide in the aquatic environment. The rate of biodegradation is proportional to the microbial population density and the concentration of hydrogen peroxide. Typical natural concentrations of hydrogen peroxide in freshwater and sea are from a few micrograms to some tens of micrograms per litre. Degradation half-lives observed are typically of the order of some hours. The microorganism/hydrogen peroxide ratio is high and degradation is favoured because there is a substantially large amount of catalase active microbes present compared to the concentration of hydrogen peroxide. If the concentration of hydrogen peroxide is remarkably higher than natural concentrations, other factors remaining constant, the inhibitive effect of hydrogen peroxide on naturally occurring microbes is beginning to have more influence thus giving longer half-lives. In extreme cases the toxicity of hydrogen peroxide will slower the degradation process remarkably (test by L'Air Liquide 1991).
Shortest half-lives <<1d can be found in surface waters of eutrophic lakes. These tests are carried out in summer time in warm surface waters and do not represent very well average degradation rates in natural waters of more unfavourable conditions and seasons. Half-lives of 1-3 days may represent quite well annual average degradation rate in mesotrophic/oligotrophic surface waters with low microbial density. Longest half-lives can be found in oligotrophic cold waters with low microbial density and low transition metal concentrations (Fe/Mn). A half-life of 5 days in surface water has been estimated to represent realistic (worst case) half-life in surface water.
As a conclusion half-lives of 2 minutes and 5 days in STP and in surface water, respectively, will be used in the risk assessment.”
The biodegradation of the substance in sediment is of no relevance as hydrogen peroxide will not partition into sediments. The degradation of hydrogen peroxide in soil is expected to be fast in the presence of organic material with half-lives of a few minutes. However, degradation may be slower in soils with low bioactivity and a half-life of 12 hours for biodegradation in soil is considered as a reasonable worst case in the present assessment.
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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