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Diss Factsheets
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EC number: 915-730-3 | 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 soil
Administrative data
Link to relevant study record(s)
Description of key information
In a study equivalent to OECD TG 307, the fate of14C-OTNE in agricultural soils was studied in microcosms according to protocols described in documents from the U.S. Food and Drug Administration of 1987(Envirogen, sponsored by IFF, 1999). Method: Samples were taken from an agricultural soil and a sludge amended agricultural soil from farms in New Jersey, USA. Sealed flasks with the soil, spiked with 10 µg test substance/g sediment dw (10 mg/kg) were incubated at laboratory ambient temperature for 12 weeks. Periodically the headspace was flushed for oxygen replenishment and the effluent gas was drawn through a train of scintillation fluids to capture volatile organics and CO2 to be determined by liquid scintillation counting. Periodically also flasks were sacrificed and exhaustively extracted with hexane/acetone. An aliquot of the solvent fraction was used for thin layer chromatography for analysis of the test substance and metabolites. The total 14C-mass balance was established for the parent and metabolites based on extraction. Results: Radiolabeled OTNE in soil is almost completely degraded after 6 weeks. After 6 weeks mineralisation (CO2 evolution) is circa 50%. After 1 to 2 weeks a range of more polar metabolites was found. After a lag time of approx. 7 days the initial rate of CO2 production was 1.4 - 1.8% /day in the sludge amended soil and in the agricultural soil, respectively. The half-life of the parent substance was estimated to be 4.2 days and 6 days in the sludge amended soil and in the agricultural soil, respectively. The half-life in agricultural soil converted to 12oC results in 11 days.
Key value for chemical safety assessment
- Half-life in soil:
- 11 d
- at the temperature of:
- 12 °C
Additional information
In a sludge amended soil the DT50 was slightly shorter: 4.2 days at 22°C and converted to 12C this results in 7.7 days.
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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