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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
Key value for chemical safety assessment
Effects on fertility
Additional information
Studies on the reproductive toxicity of hydrogen peroxide employing appropriate study methods are not available. An appropriate 90-day drinking water study with catalase deficient mice (Freeman 1997) and carcinogenicity studies with catalase deficient mice (Ito et al. 1981 a, b) and F344 rats (Takajama 1980) did not identify testes and ovaries as target organs for toxicology. Foetotoxic effects were reported from a developmental toxicity study in Wistar rats (Morijama 1982). Nevertheless the reliability of this study is questionable due to several uncertainties concerning the exposure and the effect mechanisms of hydrogen peroxide and the study cannot be used for an evaluation.
It has been shown that hydrogen peroxide is rapidly metabolised in the body to oxygen and water and does not bio-accumulate. In none of the repeated dose studies described in the dossier, hydrogen peroxide causes directly systemic effects. It is also doubtful whether hydrogen peroxide would reach inner organs as ovaries and testes as well as foetuses to cause reproductive and/or developmental toxicity. It is concluded that reproductive and developmental toxicity studies will not provide any additional useful information for the risk assessment of hydrogen peroxide and should therefore not be conducted due to animal welfare reasons.
Short description of key information:
There are no reproductive toxicity studies available employing appropriate study methods. A reliable 90-day drinking water study with catalase deficient mice (Freeman, 1997) and carginogenicity studies with catalase deficient mice (Ito, 1981 a; b) and F344 rats (Takajama, 1980) did not identify testes and ovaries as target organs for toxicology. Foetotoxic effects were reported from a developmental toxicity study in Wistar rats (Morijama, 1982). Nevertheless the reliability of this study is questionable due to several uncertainties concerning the exposure and the effect mechanisms of hydrogen peroxide and cannot be used for an evaluation.
Effects on developmental toxicity
Description of key information
There are no reproductive toxicity studies available employing appropriate study methods. A reliable 90-day drinking water study with catalase deficient mice (Freeman, 1997) and carginogenicity studies with catalase deficient mice (Ito, 1981 a; b) and F344 rats (Takajama, 1980) did not identify testes and ovaries as target organs for toxicology. Foetotoxic effects were reported from a developmental toxicity study in Wistar rats (Morijama, 1982). Nevertheless the reliability of this study is questionable due to several uncertainties concerning the exposure and the effect mechanisms of hydrogen peroxide and cannot be used for an evaluation.
Additional information
Studies on the reproductive toxicity of hydrogen peroxide employing appropriate study methods are not available. An appropriate 90-day drinking water study with catalase deficient mice (Freeman 1997) and carcinogenicity studies with catalase deficient mice (Ito et al. 1981 a, b) and F344 rats (Takajama 1980) did not identify testes and ovaries as target organs for toxicology. Foetotoxic effects were reported from a developmental toxicity study in Wistar rats (Morijama 1982). Nevertheless the reliability of this study is questionable due to several uncertainties concerning the exposure and the effect mechanisms of hydrogen peroxide and the study cannot be used for an evaluation.
It has been shown that hydrogen peroxide is rapidly metabolised in the body to oxygen and water and does not bio-accumulate. In none of the repeated dose studies described in the dossier, hydrogen peroxide causes directly systemic effects. It is also doubtful whether hydrogen peroxide would reach inner organs as ovaries and testes as well as foetuses to cause reproductive and/or developmental toxicity. It is concluded that reproductive and developmental toxicity studies will not provide any additional useful information for the risk assessment of hydrogen peroxide and should therefore not be conducted due to animal welfare reasons.
Justification for classification or non-classification
It has been shown that hydrogen peroxide is rapidly metabolised in the body to oxygen and water and does not bio-accumulate. In none of the repeated dose studies described in the dossier, hydrogen peroxide causes directly systemic effects. It is also doubtful whether hydrogen peroxide would reach inner organs as ovaries and testes as well as foetuses to cause reproductive and/or developmental toxicity. It is concluded that reproductive and developmental toxicity studies will not provide any additional useful information for the risk assessment of hydrogen peroxide and should therefore not be conducted due to animal welfare reasons.
Additional information
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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