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EC number: 211-309-7 | CAS number: 637-92-3
- 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
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- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
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- 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
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- Nanomaterial radical formation potential
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- Endpoint summary
- Stability
- Biodegradation
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- Environmental data
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- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
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- Long-term toxicity to aquatic invertebrates
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- Endocrine disrupter testing in aquatic vertebrates – in vivo
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- Sediment toxicity
- Terrestrial toxicity
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
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- Genetic toxicity
- Carcinogenicity
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- 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
A half-life of 89.5 days in soil is used in the assessment.
Key value for chemical safety assessment
- Half-life in soil:
- 89.5 d
- at the temperature of:
- 293 K
Additional information
Several studies are available for degradation of ETBE in soil. The results are conflicting. One study in which soil was polluted with gasoline containing ETBE it was shown that aerobic biodegradation was observed after the spill (Yuan, 2006). A second study showed that soil microflora that had never been in contact with ETBE before were capable of rapidly degrading the substrate, although there was some evidence that there was an adverse impact on some microflora and that only gram positive bacteria flourished under the test conditions. However, in two other studies, however, it was concluded that rapid and reliable biodegradation of ETBE in soil can not be assumed under any normal environmental conditions as very slow aerobic and anaerobic degradation in soil was observed (Yeh and Novak., 2004 and 2005). As the study by Yuan was better in design and reporting than the studies by Yeh and Novak (2004, 2005), the half-life of 89.5 days from Yuan (2006) is used in the assessment.
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