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EC number: 931-038-4 | 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
n/i-C13 -C15 –aldehydes were readily biodegradable (65% at 21 days; 10-day window met) in an OECD TG 310 assay under GLP conditions.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
n/i-C13 -C15 –aldehydes (23.6 mg/L), a mixture of n/iso C13and C15aldehydes, was tested for ready biodegradation in an OECD TG 310 assay under GLP conditions. The formation of carbon dioxide was monitored up to 28 days by analyzing the inorganic carbon (IC) which was formed from the dissolved and gaseous carbon dioxide contained in the test vessel by the addition of NaOH. The IC found was corrected for the endogenous carbon dioxide of the inoculum control. Co-incubation with 1-octanol (25.4 mg/L) was made to examine the toxicity of the n/i-C13 -C15 –aldehydes. The inoculum was obtained from a municipal wastewater treatment plant.
The results indicate that the degree of biodegradation was 65% under the test conditions within the 28-day period. The pass-level for ready biodegradation, i.e. a result of ≥60% within a 10-day window within the 28-day test period, was reached. The biodegradation of 1-octanol (25.4 mg/L in the test) was not inhibited by the n/i-C13 -C15 –aldehydes at 23.6 mg/L, i.e. there was no toxicity to microorganisms at this concentration.
In conclusion, n/i-C13 -C15 –aldehydes were shown to be readily biodegradable in a valid GLP guideline test which is considered to be suitable for assessment (Harlan, 2011).
This result is supported by the earlier observation that n/i-C13 -C15 –aldehydes are biodegradable (>60% BOD; 10 -d window not passed). However, this study was devaluated because of methodological uncertainties (Hoechst, 1995).
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