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Diss Factsheets
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EC number: - | CAS number: -
- 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 technically not feasible
- Justification for data waiving:
- other:
Reference
Description of key information
Due to the ready hydrolysis of the test item, it would be expected to exist in the environment as its hydrolysis products; boric acid and 2-propyl heptan-1-ol. These components are already registered with partition coefficients available so it was considered that further testing with respect to these components was not required. For boric acid the typical Kp for soil is given as 2.19 L/kg (log Kp=0.34 L/kg) For 2-propyl heptan-1-ol Koc is given as 562.3 (Log Koc = 2.75) The substance is predicted to be mobile in soil.
Key value for chemical safety assessment
- Koc at 20 °C:
- 562.3
Additional information
The test item could not be determined using a procedure designed to be compatible with either OECD Guideline No. 121 or EC Method C19. The test item is highly unstable in water and hydrolyses rapidly. The guidelines for the HPLC method state that the method is not applicable if the test item reacts with the mobile phase. The test item reacts with water and could potentially react with methanol as it is a protiotic solvent.
To assess the assumptions, test injections were performed. The assessment was carried out twice on separate days to confirm the observations. The parameters included:
Use of a commercially available cyanopropyl reverse phase HPLC column containing lipophilic and polar moieties
Mobile phase of methanol:water (55:45 v/v)
Gradient over 5 minutes starting at 30 minutes to 100% tetrahydrofuran
Primary detection by evaporative light scattering detector and additional check with a variable wavelength detector (210 nm).
The test item was nominally prepared at 1000 and 10000 mg/L in tetrahydrofuran (dried over anhydrous sodium sulphate)
No definitive peak(s) that represented the test item could be detected. The chromatography of the solvent blank and the test concentrations were essentially the same. The method could not be performed as the test item is decomposing before it could be analysed.
Due to the ready hydrolysis of the test item, it would be expected to exist in the environment as its hydrolysis products; boric acid and 2-propyl heptan-1-ol. These components are already registered with partition coefficients available so it was considered that further testing with respect to these components was not required. For boric acid the typical Kp for soil is given as 2.19 L/kg (log Kp=0.34 L/kg) For 2-propyl heptan-1-ol Koc is given as 562.3 (Log Koc = 2.75) The substance is predicted to be mobile in soil.
[LogKoc: 2.75]
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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