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EC number: 247-611-0 | CAS number: 26322-14-5
- 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

Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the physicochemical properties of the substance indicate that it can be expected to have a low potential for adsorption
- the study does not need to be conducted because the substance and its relevant degradation products decompose rapidly
- other:
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Information to support the waiver.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Deviations:
- yes
- Principles of method if other than guideline:
- During the preparation phase of the study problems in dissolving the test substance occurred as well as problems in detecting the test substance in an appropriate HPLC set up.
- GLP compliance:
- no
- Type of method:
- other: Information
- Radiolabelling:
- no
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- It is experimentally not possible to determine an adsorption coefficient for dihexadecyl peroxodicarbonateand thus only the calculated value can be used.
- Executive summary:
This study reveals the inpossibility to determine the partition coefficient experimentally. The outcome is used for waiving of the endpoint.
Referenceopen allclose all
The test substance appeared not to dissolve in methanol which is the recommended solvent according to OECD 121 guideline. It was observed that the test substance did dissolve in other organic solvents, like acetonitrile and tetrahydrofuran. However no significant peak detection was observed when injecting these solutions into a HPLC set up. Moreover if other solvents than methanol would be used the theoretical log Kocvalues of the reference substances would be doubtful and as a result of this the outcome of the study would also be doubtful.
Based on the calculated value of 7.6 – 8.8 for log Kocof the test substance a retention time of about 3 – 4 hours was to be expected when injecting the test substance in the HPLC test set up for the Kocdetermination. Although this value is a calculated value it was an important indication that injecting of the test substance onto the HPLC column would most probably result in very broad peak detection and by that cause also a severe contamination of the column that could hardly be removed anymore.
The above described reasons mean that it was technically not possible to determine a Kocvalue using this HPLC reference method according to OECD 121.
The alternative OECD guideline 106 for determination of adsorption and desorption of the test substance will also not be possible to conduct. The value for water solubility of the test substance was calculated to be 0.025 µg/L and the detection limit of the analytical method for the determination of the test substance was defined in the report for water solubility to be 1 µg/L. In the test set up of this adsorption/desorption study it is necessary to analyze the test substance in an aqueous phase but due to the low water solubility in combination with the determined detection limit for the analytical method this will not be possible.
The overall conclusion must be that it is experimentally not possible to determine an adsorption coefficient for the test substance and thus only the calculated value can be used.
Description of key information
The endpoint is waived: The study is technically not feasible. An estimated log Koc of 7.6 to 8.8 can be used.
Key value for chemical safety assessment
Additional information
See 26322-14-5, Adsorption on soil and sewage, Vos, 2011, SS: It is experimentally not possible to determine an adsorption coefficient for dihexadecyl peroxodicarbonate.
An estimated log Koc of 7.6 to 8.8 can be used.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

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