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Diss Factsheets
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EC number: 201-186-8 | CAS number: 79-21-0
- 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
Carcinogenicity
Administrative data
Description of key information
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The available data on carcinogenicty of peracetic acid do not meet the criteria for classification according to Regulation (EC) 1272/2008, as amended for the seventeenth time in Regulation (EU) 2021/849, and are therefore conclusive but not sufficient for classification.
Additional information
In general, Peracetic acid has no obvious structural alerts for carcinogenicity and is degraded to innocuous metabolites (water, acetic acid, oxygen).
Thus, no valid carcinogenicity study is available. According to the relevant REACH Annex testing does not appear scientifically necessary because peracetic acid is not classified as mutagen category 1, 2 or 3 and there is no evidence from the repeated dose study(ies) that it is able to induce hyperplasia and/or pre-neoplastic lesions.
In the available subchronic study in rats (Gaou, 2003), the observed toxicological effects can be attributed to the locally irritating properties and the acute toxicity of peracetic acid, i.e. irritating or corrosive effects at the site of first contact (i.e. the mucous membranes of the stomach) and decomposition to hydrogen peroxide, oxygen, and acetic acid. There are no indications of pre-neoplastic lesions and/or hyperplasia in the GI tract of the treated rats which might progress to neoplastic lesions after prolonged period of action. However, it is well known that substances which induce (sustained) local irritation can accelerate the formation of tumours at the sites of contact. This represents an effect secondary to local irritation, rather than indicating a direct carcinogenic effect. Furthermore, this is a common and general effect of many substances with irritating or corrosive properties.
A tumour initiation study was conducted in mice (Bock et al., 1975), which however is not considered valid because of several methodological and reporting deficiencies. Only females, only 30 animals per group were used; examinations were only once a week and only for skin tumours without complete gross necropsy; only one dose of peracetic acid in water without initiator was used; the negative control mice do not seem to have been treated in the same manner as the other groups, in particular the two solvents (acetone and water) seem not to have been applied. Historical control data on tumour incidence in Swiss mice is considerably higher than claimed by the author. The classification of tumours used does not correspond to the current standards.
In this study, peracetic acid was reported to act as a tumour promotor on mouse skin after initiation with DMBA (9,10-dimethyl-1,2-benzanthracene). This effect, however, is caused by sustained irritation which is due to the long-term exposure at irritating concentrations of peracetic acid in combination with a tumour initiator and is considered to be a known reaction towards corrosives, i.e. a mechanism not specific or unique to peracetic acid. If exposure is limited to sub-irritant concentrations in the absence of a tumour initiator, then there is no concern for a possible tumour-promoting effect of equilibrium peracetic acid A. Tumour promotion, as evaluated in the presence of a tumor initiator, is not likely to occur in actual human exposure scenarios.
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