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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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
- Freshwater:
EC 50 = 0.73 mg/L (OECD 202, Daphnia magna, 48 h)
- Marine water
EC50 = 0.27 mg/L (Mytilus edulis)
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.73 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 0.27 mg/L
Additional information
In an acute toxicity test on Daphnia magna performed according to OECD 202, an EC50 value of 0.73 mg/L based on PAA was determined using an equilibrium PAA concentration of 5.2 % (Gardner and Bucksath, 1996). The PAA concentration was monitored indirectly by measuring the hydrogen peroxide concentration which revealed an decrease in concentration ranging between 19 and 35 % during the test.
Five other static and one semi-static acute toxicity tests with diluted equilibrium PAA (4.5 - 15.5 %) in the fresh water flea Daphnia magna have been reported without chemical analysis. The endpoints of these tests were based on nominal peracetic acid concentrations. The 48-hour EC50 values of these tests with equilibrium products ranged between 0.48 and 1.94 mg /L based on PAA.
Two studies (Licata-Messana, 1995; Panouillères et al., 2007) have been disregarded for risk assessment because the amount of peracetic acid in the products applied was very low (0.35% and 0.15% PAA vs. 7% and 3% H2O2, respectively). It is likely that the toxicity of other components such as hydrogen peroxide, which was present at a 20 times higher concentration than PAA, were mainly responsible for the toxicity observed.
In addition to the freshwater studies mentioned above, several studies were done with salt water invertebrates. Salt water studies were conducted with brown shrimp (Crangon crangon), pacific oyster (Crassostrea gigas) and the common mussel (Mytilus edulis), (Tinsley and Sims, 1987; Butler, 1987 and Fairhurst, 1987). E(L)C50 values were 15, 0.28 and 0.27 mg/L based on PAA, respectively. Consequently, the EC50 of 0.27 mg/L for the mussel Mytilus edulis, is used as key values for marine invertebrates.
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