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Diss Factsheets
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EC number: 202-051-6 | CAS number: 91-22-5
- 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
Quinoline can be considered as readily biodegradable based on the soil study (5.2.3).
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Neither valid ready biodegradation nor inherent biodegradation test is available with quinoline. However, information is available from different tests performed either in anaerobic conditions, either from primary biodegradation tests.
An ultimate anaerobic test showed 97 % of degradation within 4 weeks with a lag time of 15 days.
Most of the available studies aim to evaluate the primary biodegradation of quinoline, and usually with adapted bacteria or enriched cultures. In these conditions, the biodegradation is very fast (100% in few days). When non adapted cultures are used, the biodegradation seems to be also fast (85% in 6.25 days at the highest tested quinoline concentration of 150 mg/L).
In anaerobic conditions, the primary degradation by unadapted freshwater sediments amounts to 100% in 45 days in sulfate-reducing conditions, and in 23 days in methanogenic conditions. The rate is much slower in denitrifying conditions (23% after 83 days). With adapted cultures, in anaerobic conditions, a total mineralisation is observed in within 48 h.
The primary degradation product identified in different studies in aerobic and anaerobic conditions is 2 -hydroxyquinoline. Another possible degraation product is 2,3 -dihydroxyquinoline observed in aerobic conditions.
In the part 5.2.3, a study in soil is presented showing a very quick and total mineralisation of quinoline. According to the Guidance on information requirements and chemical safety assessment, chapter R7b page 192 (version 1.1, May 2008), the ready biodegradation can be deduced from a study on soil because the biodegradation rate is usually slower in soil than in aquatic media, specially for sorptive substances. This assumption is strengthened by the study performed by Smith (1992) with marine sediments, showing that addition of clays reduce the quinoline degradation rate due to adsorption.
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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