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EC number: 200-889-7 | CAS number: 75-65-0
- 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
An inherent biodegradability study using adapted inoculum was considered the key study.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable, not fulfilling specific criteria
Additional information
Several studies on ready biodegradability of tertiary butyl alcohol have been conducted with results varying from little or no degradation to 99% degradation. An early publication comparing biodegradability of many chemicals in various tests of ready and inherent biodegradability included data on tertiary butanol (source and purity unspecified) showing evidence of DOC removal but not of mineralization (e.g. in a Sturm test 32% DOC removal but 0% CO2 production): it concluded that DOC loss in various tests may have been due, at least in part, to volatilisation (Gerike and Fischer, Ecotoxicology and Environmental Safety 3, 159-173, 1979). Two guideline and GLP-compliant studies of ready biodegradability were considered reliable for inclusion in the registration dossier: an effective absence of mineralisation (2.6 – 5.1% biodegradation as indicated by CO2 production) was reported in an OECD 301B study, while 99% removal of DOC was reported in an EC C.4-A die-away test. Consideration of the properties of tertiary butyl alcohol led to selection of the OECD 301B study as the key indicator for ready biodegradability: its vapour pressure is quite high and QSAR (EPIWIN v4.10) calculation based on molecular structure and physical properties of the substance indicate moderate volatility, despite its miscibility in water (predicted half-life in river water 2.4 days). The C.4-A die-away study used test flasks part filled with medium, loosely closed and shaken for 28 days: noting the possibility of DOC loss by volatilization, Part I of the C.4-A test guideline says “Moderately volatile chemicals may be tested by the DOC Die-Away method if there is sufficient gas space in the test vessels (which should be suitably stoppered). In this case, an abiotic control must be set up to allow for any physical loss”: the reported study did not include such controls
Subsequently, an inherent biodegradability study designed to prevent test material loss from volatilisation and using adapted inoculum was performed. Using the CONCAWE test method (ISO 24593, OECD draft guideline 302D), mineralisation in the presence of an adapted microbial inoculum was monitored by measurement of inorganic carbon (arising via CO2 production) in the headspace of sealed test vessels. Biodegradation began after 7 days and reached a plateau within 28 days: the level of degradation recorded (66% on day 28, mean over days 28-56 62%) demonstrates inherent and ultimate biodegradability under the criteria set in the test method. However REACH guidance considers only two different test methods (OECD 302B and 302C: passmark 70% biodegradation) for assessment of inherent biodegradability and for these methods sets time limits within which an inherent biodegradability passmark must be attained (7 and 14 days) before a degradation rate can be modelled as “inherently biodegradable meeting criteria”. Accepting these stringent criteria, tertiary butyl alcohol is designated “inherently biodegradable not meeting criteria”
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