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EC number: 222-321-7 | CAS number: 3425-61-4
- 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
There is no test performed with Tert-amyl hydroperoxide. The acute toxic effects on aquatic invertebrates of this substance are read-across from data obtained with1,1,3,3-Tetramethylbutyl hydroperoxide: an acute toxicity test to Daphnia magna was conducted in accordance with OECD test guidelines and with the OECD Principles of Good Laboratory Practice: EC50-48h = 6.7 m/L (Measured Mean).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 6.7 mg/L
Additional information
- Immobilization in the control did not exceed 10%
- Oxygen concentration did not fall below 3 mg/L at any point during the study
- The EC50 value of the reference compound, potassium dichromate, was in the range of 0.25-2.0 mg/L (Documented as part of GLP laboratory maintenance).
- No daphnids were trapped on the surface for any length of time.
- The analytical validity criteria set in the study plan were met.
There is no test performed with Tert-amyl hydroperoxide. The toxic effects on aquatic invertebrates of this substance is read-across from data obtained with1,1,3,3-Tetramethylbutyl hydroperoxide.
In order to predict the effects of 1,1,3,3-Tetramethylbutyl Hydroperoxide in an aquatic environment, an acute toxicity test to Daphnia magna was conducted in accordance with OECD test guidelines and with the OECD Principles of Good Laboratory Practice.
The toxicity of the test chemical and any formed degradation products to juvenile daphnia was determined in a static system over an exposure period of 48 hours. The following concentrations were tested 0.6, 1.4, 3.0, 6.8 and 15 mg/L. The NOEC was determined as 4.21 mg/L (Measured Mean Concentration). The EC50 (48h) was calculated as 6.7 mg/l. (Measured Mean).
Chemical analysis was conducted at the start and at the end of the study. Analytical quality criteria were met. Geometric measured mean concentrations were calculated for use in the end point calculations.
The following quality criteria were met in the final definitive study:
The following quality criterion was not met:
The test substance did not remain stable during the test.
Investigation of the effects of the non readily biodegradable degradation products would benefit further risk assessment of this substance
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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