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EC number: 276-431-5 | CAS number: 72162-23-3 The high-boiling fraction separated by distillation from the products obtained from the reaction of nitric acid with cyclododecanol and cyclododecanone. Composed primarily of dodecanedioic acid, undecanedioic acid, and sebacic acid.
- 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

Partition coefficient
Administrative data
Link to relevant study record(s)
Description of key information
Stock solutions of the reference substances (except for ethylmethylketone) at concentrations of approximately 1 g/l in methanol were used. The stock solutions and pure ethylmethylketone were diluted to obtain an end solution of mobile phase (pH 2 or pH 7).
A 1260 mg/l stock solution of the test substance was prepared in methanol. The stock solution was diluted to obtain an end solution of mobile phase pH 2. The final concentration of the test substance solution was 756 mg/l.
A 936 mg/l stock solution of the test substance was prepared in methanol. The stock solution was diluted to obtain an end solution of mobile phase pH 7. The final concentration of the test substance solution was 702 mg/l.
A 5.61 g/l stock solution of the unretained component formamide (99.8%) in methanol was used. The stock solution was diluted to obtain an end solution of mobile phase (pH 2 or pH 7).
PERFORMANCE OF THE TEST
The reference substance and test substance solutions were injected in duplicate. Blank solutions (mobile phase pH 2 or pH 7) were analysed by single injection. The capacity factor (k') of each compound was calculated from its retention time. The log k` values of the references substances were plotted against the known log Pow values. A linear regression program was used to calculate the calibration curve. Linear regression analysis was performed using the least squares method. The log Pow value for the test substance was calculated by substituting its mean log k` in the calibration curve.
Key value for chemical safety assessment
Additional information
The log Pow of the different components in Corfree® M1 diacid mixture at pH 2 and 35°C ranges from < 0.3 to 2.1 (HPLC method). At pH 2, the substance is not-ionised.
The log Pow of the different components in Corfree® M1 diacid mixture at pH 7 and 35°C are < 0.3 (HPLC method). At pH 7, the substance is ionised.
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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