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EC number: 201-696-0 | CAS number: 86-74-8
- 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 and sediment: simulation tests
Administrative data
Link to relevant study record(s)
Description of key information
Adapted bacteria are able to biodegrade carbazole to some degree.
In a primary biodegradation test using adapted microorganism prepared from creosote contaminated soil by extraction in phosphate buffer, 58.6 and 65.5 % degradation were observed after 3 and 14 days respectively (Mueller 1991).
23.6% of the applied radioactivity (14C labeled carbazole) was determined as radiolabeled CO2 in a biodegradation test using a bacterial population as inoculums which was grown on crude oil as sole carbon source for some years and crude oil as sole substrate amended with a minimal amount of 14C labeled carbazole (Foght 1989).
Key value for chemical safety assessment
Additional information
The biodegradation capability of different bacterial populations adapted to creosote and crude oil, each of them containing carbazole, are investigated in two studies.
Mueller 1991
In creosote contaminated groundwater containing carbazole as minor constituent, primary biodegradation of carbazole was demonstrated using adapted microorganisms prepared from creosote contaminated surface soil as inoculum. For carbazole, 58.6 and 65.5% primary biodegradation was determined by test substance analysis (extraction from test medium and GC analysis) after 3 and 14 days, respectively.
Foght 1989
Biodegradation tests were conducted with 6 pure bacterial cultures capable of degrading saturated alkanes, with 3 pure bacterial cultures capable of degrading aromatic compounds and with a mixed bacterial population grown on crude oil. Bacteria of pure cultures were isolated from marine sediment or water (1 each), from fresh water (5), from waste water (1) and from soil (1).
Each bacterial culture was tested with crude oil as substrate. Crude oil was amended in individual tests by 14C labeled constituents representing straight chain alkanes, polycyclic aromatic hydrocarbons, and nitrogen heterocyclic compounds. Biodegradation was determined counting the radioactivity of CO2 transferred from the incubation medium into scintillation vials.
In the biodegradation test with the oil adapted mixed bacterial culture as inoculum and 14C labeled carbazole amended to crude oil, 23.6% biodegradation was determined by the formation of radioactive CO2 after 14 days.
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